JP2009279489A - Method of purifying contaminated soil and/or ground water - Google Patents

Method of purifying contaminated soil and/or ground water Download PDF

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JP2009279489A
JP2009279489A JP2008132082A JP2008132082A JP2009279489A JP 2009279489 A JP2009279489 A JP 2009279489A JP 2008132082 A JP2008132082 A JP 2008132082A JP 2008132082 A JP2008132082 A JP 2008132082A JP 2009279489 A JP2009279489 A JP 2009279489A
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nutrient source
well
inner cylinder
groundwater
nutrient
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Koji Shimizu
巧治 清水
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Panasonic Corp
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<P>PROBLEM TO BE SOLVED: To provide a method of purifying contaminated soil and/or ground water which enables improvement in purifying efficiency. <P>SOLUTION: A nutrient source feed well 10 which has an inside cylinder 12 arranged within a well casing 11 is formed. The inside cylinder 12 has a bottom surface, and its bottom or side surface has two or more holes of a maximum diameter of 1-2 mm. The inside cylinder 12 is arranged with a separation space between the bottom surface of the well 10 and the side surface of the well casing 11. A nutrient source 14 is injected into the inside cylinder 12. The nutrient source 14 contains hexitol and glycerine and has a viscosity at 10°C of ≥0.2 Pa×S. <P>COPYRIGHT: (C)2010,JPO&INPIT

Description

本発明は、汚染土壌及び/又は地下水の浄化方法に関する。   The present invention relates to a method for purifying contaminated soil and / or groundwater.

近年、工業廃水などに含まれる、トリクロロエチレン(TCE)、テトラクロロエチレン(PCE)、テトラクロロエタンなどの有機塩素化合物などによる環境汚染が大きな問題となっている。これらの汚染物質の多くは、土壌中に浸透して地下水に混入し、この地下水を通じて汚染領域を拡大させる。このような環境汚染の拡大を防止するとともに、汚染された土壌・地下水を浄化し、修復する技術の確立が強く望まれている。   In recent years, environmental pollution due to organic chlorine compounds such as trichlorethylene (TCE), tetrachloroethylene (PCE), and tetrachloroethane, which are included in industrial wastewater, has become a major problem. Many of these pollutants penetrate into the soil and enter groundwater, expanding the contaminated area through this groundwater. It is strongly desired to establish a technology for preventing the spread of environmental pollution and purifying and repairing contaminated soil and groundwater.

汚染土壌及び地下水の浄化方法として、近年、微生物による生物学的な処理を用いた方法(バイオレメディエーション)が提案されている。バイオレメディエーションは、汚染領域に生息する微生物や外部から汚染領域に導入された微生物によって、汚染物質を無害な物質にまで分解する方法である。バイオレメディエーションにおいて、微生物の栄養源を土壌・地下水に供給し、微生物を活性化させて汚染物質の分解を促進させることが提案されている。微生物の栄養源としては、例えば、ソルビトール、グリセリン及びマンニトールから選択される有機物と、炭素数12以上の脂肪酸等の有機物と、カルシウム化合物とを含む組成物が提案されている(特許文献1)。
特許第3815464号明細書
In recent years, methods (bioremediation) using biological treatment with microorganisms have been proposed as methods for purifying contaminated soil and groundwater. Bioremediation is a method of decomposing pollutants into innocuous substances by microorganisms that live in contaminated areas or introduced from outside into contaminated areas. In bioremediation, it has been proposed to supply microorganism nutrients to soil and groundwater to activate microorganisms and promote degradation of pollutants. As a nutrient source for microorganisms, for example, a composition containing an organic substance selected from sorbitol, glycerin and mannitol, an organic substance such as a fatty acid having 12 or more carbon atoms, and a calcium compound has been proposed (Patent Document 1).
Japanese Patent No. 3815464

バイオレメディエーションにおいて、栄養源を土壌中に長期間とどまらせ、微生物を持続的に活性化することが求められている。しかしながら、ソルビトールを主成分とする液状の栄養源は拡散性が優れるため、注入した栄養源が地下水流によって汚染領域から短時間で流出するという問題があった。そこで、本発明は、栄養源、特にソルビトールを主成分とする栄養源を徐々に注入可能な新たな注入方法を用いた汚染土壌及び/又は地下水の浄化方法を提供する。   In bioremediation, it is required to keep the nutrient source in the soil for a long time and to continuously activate the microorganisms. However, since the liquid nutrient source mainly composed of sorbitol has excellent diffusibility, there is a problem that the injected nutrient source flows out of the contaminated area in a short time by the groundwater flow. Therefore, the present invention provides a method for purifying contaminated soil and / or groundwater using a new injection method capable of gradually injecting a nutrient source, particularly a nutrient source mainly composed of sorbitol.

本発明の汚染土壌及び/又は地下水を浄化する方法(以下、「本発明の浄化方法」ともいう)は、井戸ケーシング内に内筒が配置された栄養源供給井戸を形成すること、及び、前記内筒に栄養源を注入することを含み、前記栄養源は、ヘキシトール及びグリセリンを含み、栄養源の粘度(10℃)は、0.2Pa・S以上であり、前記内筒は、最大径が0.5〜2.5mmである孔を複数備える側面及び底面を有し、かつ、前記井戸の底面及び前記井戸ケーシングの側面と離隔空間をもって配置されている浄化方法である。   The method for purifying contaminated soil and / or groundwater of the present invention (hereinafter also referred to as “the purification method of the present invention”) includes forming a nutrient source supply well in which an inner cylinder is disposed in a well casing, and Injecting a nutrient source into the inner cylinder, the nutrient source includes hexitol and glycerin, the nutrient source has a viscosity (10 ° C.) of 0.2 Pa · S or more, and the inner cylinder has a maximum diameter. The purification method has a side surface and a bottom surface having a plurality of holes of 0.5 to 2.5 mm, and is disposed with a space apart from the bottom surface of the well and the side surface of the well casing.

本発明の浄化方法によれば、内筒からヘキシトールを徐々に放出可能である。このため、本発明の浄化方法によれば、例えば、微生物を持続的に活性化させることができ、汚染土壌及び地下水の浄化効率を向上できる。   According to the purification method of the present invention, hexitol can be gradually released from the inner cylinder. For this reason, according to the purification method of this invention, for example, microorganisms can be activated continuously and the purification efficiency of contaminated soil and groundwater can be improved.

本発明は、所定の径を有する孔を備える内筒が配置された二重構造の栄養源供給井戸を設け、その内筒を通じて所定の粘度を有する栄養源の供給を行えば、栄養源を内筒からゆっくり放出させることができること、及び、放出された栄養源が井戸内の地下水に希釈され栄養源の拡散を促進できるという知見に基づく。また、所定の粘度を有する栄養源をそのまま井戸内に配置すると、ヘキシトールの自然分解を抑制でき、ヘキシトールの分解物を栄養源とする微生物であって、汚染物質の浄化への寄与が少ない又は寄与がない微生物(とりわけ、好気性微生物)の増殖を抑制できることから、揮発性有機物(とりわけ、PCE及びTCE)の分解に寄与する嫌気性微生物(例えば、Dehalococcoides ethenogenesなど)の増殖及び/又は活性化を効率よく促進できるという知見に基づく。   The present invention provides a nutrient source supply well having a double structure in which an inner cylinder having a hole having a predetermined diameter is arranged, and supplying the nutrient source having a predetermined viscosity through the inner cylinder. It is based on the knowledge that it can be released slowly from the cylinder and that the released nutrient source can be diluted in the groundwater in the well to promote the diffusion of the nutrient source. In addition, if a nutrient source having a predetermined viscosity is placed in the well as it is, it can suppress the natural decomposition of hexitol and is a microorganism that uses a decomposition product of hexitol as a nutrient source, and contributes little to or contributes to the purification of pollutants. The growth and / or activation of anaerobic microorganisms (eg, Dehalococides ethenegenes) that contribute to the degradation of volatile organics (especially PCE and TCE) can be suppressed because the growth of microorganisms (especially aerobic microorganisms) that are free of odor is possible. Based on the knowledge that it can be promoted efficiently.

すなわち、本発明の浄化方法は、井戸ケーシング内に内筒が配置された栄養源供給井戸を形成すること、及び、内筒に栄養源を注入することを含み、栄養源は、ヘキシトール及びグリセリンを含み、栄養源の粘度(10℃)は、0.2Pa・S以上であり、内筒は、最大径が0.5〜2.5mmである孔を複数備える側面及び底面を有し、かつ、井戸の底面及び井戸ケーシングの側面と離隔空間をもって配置されている浄化方法である。   That is, the purification method of the present invention includes forming a nutrient source supply well in which an inner cylinder is disposed in a well casing, and injecting the nutrient source into the inner cylinder, and the nutrient source includes hexitol and glycerin. And the viscosity of the nutrient source (10 ° C.) is 0.2 Pa · S or more, the inner cylinder has a side surface and a bottom surface including a plurality of holes having a maximum diameter of 0.5 to 2.5 mm, and It is the purification method arrange | positioned with the bottom face of a well, the side surface of a well casing, and separation space.

本発明の浄化方法によれば、栄養源を内筒から徐々に放出できるため、微生物を持続的に活性化できる。また、内筒から栄養源を徐々に放出できることから、栄養源を汚染領域に長期間滞留させることができ、さらには、栄養源を内筒に一回充填することにより、長期間微生物を活性化することができる。したがって、本発明の浄化方法によれば、汚染土壌及び地下水の浄化効率を向上できる。また、本発明の浄化方法によれば、例えば、液状の栄養源を希釈することなく使用できるため、希釈の装置や手間が省け、簡便である。さらに、本発明の浄化方法によれば、炭素鎖の長い(炭素数の多い)状態で栄養源を供給するため、孔付近における微生物の過剰な増殖を抑制でき、孔が閉塞されることなく汚染領域に栄養源を拡散させることができる。   According to the purification method of the present invention, the nutrient source can be gradually released from the inner cylinder, so that the microorganisms can be activated continuously. In addition, since the nutrient source can be gradually released from the inner cylinder, the nutrient source can be retained in the contaminated area for a long time, and further, the microorganism can be activated for a long time by filling the inner cylinder once with the nutrient source. can do. Therefore, according to the purification method of the present invention, the purification efficiency of contaminated soil and groundwater can be improved. Further, according to the purification method of the present invention, for example, since a liquid nutrient source can be used without diluting, the apparatus and labor for diluting can be saved and it is simple. Furthermore, according to the purification method of the present invention, the nutrient source is supplied in a state where the carbon chain is long (the number of carbon atoms is large), so that excessive growth of microorganisms in the vicinity of the pore can be suppressed, and contamination is prevented without blocking the pore. Nutrient sources can be spread throughout the area.

[栄養源供給井戸]
本発明において「栄養源供給井戸」とは、汚染土壌及び/又は地下水に栄養源を供給するため井戸であって、井戸ケーシング内に内筒が配置された井戸のことをいう。
[Nutrition source supply well]
In the present invention, the “nutrient source supply well” refers to a well for supplying a nutrient source to contaminated soil and / or groundwater and having an inner cylinder disposed in a well casing.

[内筒]
本発明において「内筒」とは、最大径が0.5〜2.5mmである孔を複数備える側面及び底面を有するものをいう。内筒の底面に孔を備えることから、例えば、比重が地下水よりも重い栄養源を下部不透水層付近に自然希釈及び/又は拡散させることができる。内筒は、内部に栄養源を配置可能であり、底面及び側面から内筒の外部に栄養源を拡散可能であるものが好ましい。内筒の孔の最大径は、0.5〜2.5mmであり、徐放性及び拡散性を向上させる点から1.0〜2.0mmが好ましい。本発明において「最大径」とは、孔の外周のある点とその他の点とを結ぶ線のうち最も長い線の長さのことをいう。孔の形状が円形である場合、最大径は孔の直径となり、孔の形状が矩形の場合、最大径は孔の対角線の長さとなる。孔の最大径は、従来公知の方法によって測定できる。孔の形状としては、例えば、円形及び角形等が挙げられ、中でも、目詰まり抑制の点から、内筒の軸方向と直交方向に長軸を有する横長の楕円及び四角形が好ましい。孔は、内筒全体に形成されていても良いし、底面と地下水と接触する側面とにのみ形成されていても良い。孔の形成密度は、栄養源の拡散の均一性の点から、底面と反対側の端部(上端部)側よりも底面側の方が疎である(小さい)ことが好ましい。孔の面積は、例えば、0.2〜4.9mm2であり、好ましくは0.7〜3.2mm2である。孔の形成密度は、底面側から連続的に大きくしても良いし、段階的に大きくしても良い。内筒の開口率は、例えば、50〜85%であり、60〜80%が好ましい。内筒の厚みは、例えば、1〜2mmである。内筒は、例えば、複数の孔を有する樹脂又は鋼材等により形成できる。
[Inner cylinder]
In the present invention, the “inner cylinder” means one having a side surface and a bottom surface provided with a plurality of holes having a maximum diameter of 0.5 to 2.5 mm. Since a hole is provided in the bottom surface of the inner cylinder, for example, a nutrient source whose specific gravity is heavier than that of groundwater can be naturally diluted and / or diffused near the lower impermeable layer. The inner cylinder is preferably capable of disposing a nutrient source inside and capable of diffusing the nutrient source from the bottom and side surfaces to the outside of the inner cylinder. The maximum diameter of the hole in the inner cylinder is 0.5 to 2.5 mm, and 1.0 to 2.0 mm is preferable from the viewpoint of improving sustained release and diffusibility. In the present invention, the “maximum diameter” means the length of the longest line among lines connecting a point on the outer periphery of the hole and other points. When the hole shape is circular, the maximum diameter is the diameter of the hole, and when the hole shape is rectangular, the maximum diameter is the length of the diagonal line of the hole. The maximum diameter of the hole can be measured by a conventionally known method. Examples of the shape of the hole include a circular shape and a rectangular shape. Among them, a horizontally long ellipse and a rectangle having a long axis in a direction orthogonal to the axial direction of the inner cylinder are preferable from the viewpoint of suppressing clogging. The hole may be formed in the entire inner cylinder, or may be formed only on the bottom surface and the side surface that contacts the groundwater. The pore formation density is preferably sparser (smaller) on the bottom surface side than on the end portion (upper end portion) side opposite to the bottom surface, from the point of uniformity of nutrient source diffusion. The area of the hole is, for example, 0.2 to 4.9 mm 2 , and preferably 0.7 to 3.2 mm 2 . The formation density of the holes may be increased continuously from the bottom surface side or may be increased stepwise. The opening ratio of the inner cylinder is, for example, 50 to 85%, and preferably 60 to 80%. The thickness of the inner cylinder is, for example, 1 to 2 mm. The inner cylinder can be formed of, for example, a resin or a steel material having a plurality of holes.

内筒は、栄養源供給井戸の底面及び井戸内の井戸ケーシングの側面と離隔空間をもって配置される。本発明において「離隔空間をもって配置される」とは、ある一定の距離を保って離れた状態で配置されることをいう。したがって、内筒の底面と井戸の底面との間、内筒の外周面と井戸ケーシングの内周面との間にそれぞれ空間が形成される。内筒の底面と井戸底面との間に空間を形成することにより、例えば、比重が地下水よりも重い栄養源を下部不透水層付近に自然希釈及び/又は拡散させることができる。内筒の底面と井戸底面との距離は、30〜50mmが好ましい。また、内筒の側面(外周側)と井戸ケーシングの側面(内周側)との距離は、栄養源の注入量により適宜決定されるが、井戸ケーシングの直径の1/6程度であることが好ましい。内筒は、栄養源を均一に拡散させる点から、井戸ケーシングと略同心で配置されていることが好ましい。   The inner cylinder is arranged with a space apart from the bottom surface of the nutrient source supply well and the side surface of the well casing in the well. In the present invention, “arranged with a separation space” means that they are arranged in a state of being separated at a certain distance. Accordingly, spaces are formed between the bottom surface of the inner cylinder and the bottom surface of the well, and between the outer peripheral surface of the inner cylinder and the inner peripheral surface of the well casing. By forming a space between the bottom surface of the inner cylinder and the bottom surface of the well, for example, a nutrient source whose specific gravity is heavier than groundwater can be naturally diluted and / or diffused in the vicinity of the lower impermeable layer. The distance between the bottom surface of the inner cylinder and the bottom surface of the well is preferably 30 to 50 mm. Moreover, although the distance of the side surface (outer peripheral side) of an inner cylinder and the side surface (inner peripheral side) of a well casing is suitably determined by the injection amount of a nutrient source, it should be about 1/6 of the diameter of a well casing. preferable. It is preferable that the inner cylinder is arranged substantially concentrically with the well casing from the viewpoint of uniformly diffusing nutrient sources.

井戸ケーシングは、通常の揚水井戸及び栄養源供給井戸等に使用される公知の井戸ケーシングが使用できる。井戸ケーシングは、井戸内への地下水の流出入可能であれば良く、例えば、透水性の材質、複数の孔を有する樹脂又は鋼材等により形成されたスクリーンを備える。井戸内への土壌の流入を抑制する点から、少なくとも透水層内に配置される部分にスクリーンが形成された井戸ケーシングが好ましい。   As the well casing, known well casings used for ordinary pumping wells, nutrient source supply wells, and the like can be used. The well casing is only required to be able to flow into and out of the groundwater, and includes, for example, a screen formed of a water-permeable material, a resin having a plurality of holes, a steel material, or the like. From the viewpoint of suppressing the inflow of soil into the well, a well casing in which a screen is formed at least in a portion disposed in the permeable layer is preferable.

[栄養源]
本発明において「栄養源」とは、微生物を活性化するための物質であって、ヘキシトール及びグリセリンを含む。栄養源の粘度(10℃)は、栄養源を内筒から徐放させる点から0.2Pa・S(×1000cp)以上であり、好ましくは0.3〜0.95Pa・S、より好ましくは略0.9Pa・Sである。粘度の測定は、例えば、B型粘度計を用いて行うことができる。
[Nutrition source]
In the present invention, the “nutrient source” is a substance for activating microorganisms, and includes hexitol and glycerin. The viscosity (10 ° C.) of the nutrient source is 0.2 Pa · S (× 1000 cp) or more, preferably 0.3 to 0.95 Pa · S, more preferably about from the point that the nutrient source is gradually released from the inner cylinder. 0.9 Pa · S. The viscosity can be measured using, for example, a B-type viscometer.

ヘキシトールとしては、例えば、ソルビトール、マンニトール等が挙げられ、中でも、グリセリンとの親和性の点から、ソルビトールが好ましい。栄養源の主成分はヘキシトールであることが好ましく、より好ましくはソルビトールである。栄養源におけるヘキシトールの含有量は、例えば、微生物の活性化及び徐放性向上の点から40〜70重量%が好ましく、より好ましくは50〜65重量%である。栄養源におけるグリセリンの含有量は、徐放性を向上させる点から5〜20重量%が好ましく、より好ましくは7〜15重量%である。栄養源としては、ヘキシトール略60重量%、グリシトール10重量%を含む栄養源が好ましい。   Examples of hexitol include sorbitol, mannitol and the like. Among them, sorbitol is preferable from the viewpoint of affinity with glycerin. The main component of the nutrient source is preferably hexitol, more preferably sorbitol. The content of hexitol in the nutrient source is, for example, preferably 40 to 70% by weight, more preferably 50 to 65% by weight from the viewpoint of activating microorganisms and improving sustained release. The content of glycerin in the nutrient source is preferably 5 to 20% by weight, more preferably 7 to 15% by weight from the viewpoint of improving sustained release. As a nutrient source, a nutrient source containing approximately 60% by weight hexitol and 10% by weight glycitol is preferable.

栄養源は、さらに水を含んでも良い。栄養源における水の含有量は、例えば、徐放性の点から35重量%以下であり、好ましくは20〜30重量%である。その他の成分として、例えば、シルト質の土層や汚染物質の溜まり部分への浸透性を向上させる点から、ポリオキシエチレンソルビタン脂肪酸エステルをさらに含んでも良く、中でもポリオキシエチレングリコール(20)−ソルビタン−モノオレート(ポリソルベート20)が好ましい。栄養源におけるポリオキシエチレンソルビタン脂肪酸エステルの含有量は、例えば、0〜10重量%であり、好ましくは1〜5重量%である。栄養源は、例えば、内筒の孔及び井戸ケーシングのスクリーンの目詰まり及び地下水面の上昇抑制の点から、さらにクエン酸を含んでも良い。   The nutrient source may further include water. The content of water in the nutrient source is, for example, 35% by weight or less, and preferably 20-30% by weight from the viewpoint of sustained release. As other components, for example, polyoxyethylene sorbitan fatty acid ester may be further included from the viewpoint of improving the permeability to a silty soil layer or a reservoir of contaminants, and in particular, polyoxyethylene glycol (20) -sorbitan -Monooleate (polysorbate 20) is preferred. The content of the polyoxyethylene sorbitan fatty acid ester in the nutrient source is, for example, 0 to 10% by weight, and preferably 1 to 5% by weight. The nutrient source may further contain, for example, citric acid from the viewpoint of clogging of the holes of the inner cylinder and the screen of the well casing and suppressing the rise of the groundwater surface.

栄養源は市販品を使用してよい。市販品としては、例えば、アムテクリーンP SL6−90SRW(商品名、松下電器産業株式会社製、成分:ソルビトール約60%、グリセリン約10%、ポリオキシエチレン(20)ソルビタンモノオレート約2%、水約28%、粘度(10℃):約0.90Pa・S、粘度(20℃):約0.34Pa・S)が挙げられる。   A commercially available product may be used as the nutrient source. Examples of commercially available products include Amteclean P SL6-90SRW (trade name, manufactured by Matsushita Electric Industrial Co., Ltd., components: about 60% sorbitol, about 10% glycerin, about 2% polyoxyethylene (20) sorbitan monooleate, about about water. 28%, viscosity (10 ° C.): about 0.90 Pa · S, viscosity (20 ° C.): about 0.34 Pa · S).

[汚染土壌及び/又は地下水]
本発明において「汚染土壌及び/又は地下水」とは、汚染物質を含む土壌及び地下水のことをいう。汚染物質としては、例えば、揮発性有機化合物(VOC)、重金属、油分、硝酸性窒素、亜硝酸性窒素等が挙げられる。揮発性有機化合物としては、例えば、有機塩素化合物、ベンゼン、ホルムアルデヒド、トルエン、キシレン等が挙げられる。中でも、本発明の浄化方法は、揮発性有機化合物、より好適には有機塩素化合物を含む汚染土壌及び/又は地下水の浄化に適している。有機塩素化合物としては、例えば、四塩化炭素、1,2−ジクロロエタン、1,1−ジクロロエチレン、cis−1,2−ジクロロエチレン、1,3−ジクロロプロペン、ジクロロメタン、テトラクロロエチレン(PCE)、1,1,1−トリクロロエタン、1,1,2−トリクロロエタン、トリクロロエチレン(TCE)等が挙げられる。中でも、本発明の浄化方法は、テトラクロロエチレン、トリクロロエチレン、cis−1,2−ジクロロエチレン、1,1−ジクロロエチレン及び塩化ビニル等で汚染された土壌及び/又は地下水の浄化に特に適している。
[Contaminated soil and / or groundwater]
In the present invention, “contaminated soil and / or groundwater” refers to soil and groundwater containing pollutants. Examples of pollutants include volatile organic compounds (VOC), heavy metals, oils, nitrate nitrogen, nitrite nitrogen, and the like. Examples of volatile organic compounds include organic chlorine compounds, benzene, formaldehyde, toluene, xylene, and the like. Among these, the purification method of the present invention is suitable for the purification of contaminated soil and / or groundwater containing a volatile organic compound, more preferably an organic chlorine compound. Examples of the organic chlorine compound include carbon tetrachloride, 1,2-dichloroethane, 1,1-dichloroethylene, cis-1,2-dichloroethylene, 1,3-dichloropropene, dichloromethane, tetrachloroethylene (PCE), 1,1, Examples thereof include 1-trichloroethane, 1,1,2-trichloroethane, trichlorethylene (TCE) and the like. Among these, the purification method of the present invention is particularly suitable for purification of soil and / or groundwater contaminated with tetrachloroethylene, trichloroethylene, cis-1,2-dichloroethylene, 1,1-dichloroethylene, vinyl chloride, and the like.

[浄化方法]
本発明の浄化方法では、まず、栄養源供給井戸を形成する。栄養源供給井戸は、例えば、ボーリング等により採掘した孔の壁面に井戸ケーシングを形成し、その内部に内筒を配置することによって形成できる。栄養源供給井戸は、栄養源の拡散を向上でき、微生物を効率的に活性化できる点から、少なくとも透水層下部まで達していることが好ましく、その透水層の下に位置する不透水層まで達していることがより好ましい。なお、本発明において「透水層」とは、地下水が存在する層をいい、帯水層、飽和層、宙水層を含む。
[Purification method]
In the purification method of the present invention, first, a nutrient source supply well is formed. The nutrient source supply well can be formed, for example, by forming a well casing on the wall surface of a hole mined by boring or the like, and disposing an inner cylinder therein. It is preferable that the nutrient source supply well reaches at least the lower part of the permeable layer from the viewpoint of improving the diffusion of the nutrient source and efficiently activating the microorganisms, and reaches the impermeable layer located below the permeable layer. More preferably. In the present invention, the “permeable layer” refers to a layer in which groundwater exists, and includes an aquifer layer, a saturated layer, and an aquifer layer.

栄養源供給井戸の直径は、汚染領域の大きさ、汚染物質の濃度及び種類等により適宜決定でき、例えば、100〜150mmが好ましい。内筒の直径は、栄養源供給井戸の直径、汚染領域の大きさ、汚染物質の濃度及び種類等により適宜決定でき、例えば、65〜100mmが好ましく、栄養源供給井戸の直径の2/3であることがより好ましい。井戸の直径が100〜150mmである場合、内筒の直径を65〜100mm、内筒の外周面と井戸ケーシングの内周面との距離を17〜50mm、内筒の底面と井戸の底面との距離を50〜80mmとすることが好ましい。   The diameter of the nutrient source supply well can be appropriately determined depending on the size of the contaminated area, the concentration and type of the contaminant, and is preferably 100 to 150 mm, for example. The diameter of the inner cylinder can be appropriately determined depending on the diameter of the nutrient source supply well, the size of the contaminated area, the concentration and type of the contaminant, and is preferably 65 to 100 mm, for example, 2/3 of the diameter of the nutrient source supply well. More preferably. When the diameter of the well is 100 to 150 mm, the diameter of the inner cylinder is 65 to 100 mm, the distance between the outer peripheral surface of the inner cylinder and the inner peripheral surface of the well casing is 17 to 50 mm, the bottom of the inner cylinder and the bottom of the well The distance is preferably 50 to 80 mm.

栄養源供給井戸は、汚染領域内及び/又は汚染領域周辺に形成することが好ましく、汚染物質の拡散抑制の点から、汚染領域を囲むように複数形成することがより好ましい。栄養源供給井戸を効果的に浄化壁として機能させる点から、地下水流の下流側の栄養源供給井戸の間隔を、地下水流の上流側よりも狭くすることが好ましい。この場合、例えば、地下水流の下流側に位置する栄養源供給井戸の間隔を0〜50mmとし、地下水流の上流側に位置する栄養源供給井戸の間隔を50〜100mmとすることが好ましい。本発明において「汚染領域」とは、汚染物質濃度が所定の濃度以上である土壌及び/又は地下水を少なくとも含む領域のことをいう。本発明において「栄養源供給井戸の間隔」とは、栄養源供給井戸の外周のある点とそれに隣接する井戸の外周のある点とを結ぶ線であって、最短のものをいう。   Nutrient source supply wells are preferably formed in and / or around the contaminated area, and more preferably formed so as to surround the contaminated area from the viewpoint of suppressing the diffusion of contaminants. From the viewpoint of effectively functioning the nutrient source supply well as a purification wall, the interval between the nutrient source supply wells on the downstream side of the groundwater flow is preferably narrower than that on the upstream side of the groundwater flow. In this case, for example, the interval between nutrient source supply wells located on the downstream side of the groundwater flow is preferably 0 to 50 mm, and the interval between nutrient source supply wells located on the upstream side of the groundwater flow is preferably set to 50 to 100 mm. In the present invention, the “polluted area” refers to an area including at least soil and / or groundwater having a pollutant concentration equal to or higher than a predetermined concentration. In the present invention, the “interval of nutrient source supply wells” is a line connecting a point on the outer periphery of the nutrient source supply well and a point on the outer periphery of the adjacent well and is the shortest one.

つぎに、内筒に栄養源を注入する。複数の栄養源供給井戸を形成した場合、栄養源を注入する順番は特に制限されないが、上流側に位置する栄養源供給井戸における栄養源の拡散を抑制できることから、地下水流の下流側から上流側に向かって栄養源を注入することが好ましい。栄養源の注入は、ポンプ等を用いて加圧しながら行っても良いし、加圧することなく行っても良い。   Next, a nutrient source is injected into the inner cylinder. When multiple nutrient source supply wells are formed, the order of injecting the nutrient sources is not particularly limited, but the diffusion of nutrient sources in the nutrient source supply well located upstream can be suppressed, so the downstream side of the groundwater flow from the upstream side It is preferable to inject a nutrient source toward. The nutrient source may be injected while being pressurized using a pump or the like, or may be performed without being pressurized.

本発明は、その他の態様として、本発明の浄化方法に用いる栄養源供給井戸であって、少なくとも透水層下部まで達する孔に挿入された井戸ケーシングと、底面を有し、最大径が1〜2mmである孔を複数備える底面及び側面を有する内筒とを含み、前記内筒が、井戸の底面及び前記井戸ケーシングの側面と離隔空間をもって前記井戸ケーシング内に配置されている、栄養源供給井戸を含む。   As another aspect, the present invention is a nutrient source supply well used in the purification method of the present invention, having a well casing inserted into at least a hole reaching the bottom of the permeable layer, a bottom surface, and a maximum diameter of 1 to 2 mm. A nutrient source supply well, wherein the inner cylinder is disposed in the well casing with a space apart from the bottom surface of the well and the side surface of the well casing. Including.

また、本発明は、さらにその他の態様として、本発明の浄化方法及び本発明の栄養源供給井戸に使用される管であって、井戸ケーシングと、底面を有する内筒とを含み、前記内筒は、最大径が1〜2mmである孔を複数備える底面及び側面を有し、前記内筒は、前記井戸ケーシングの側面と離隔空間をもって前記井戸ケーシング内に配置可能である、栄養源供給井戸用管を含む。   Moreover, this invention is a pipe | tube used for the purification method of this invention, and the nutrient source supply well of this invention as another aspect, Comprising: A well casing and the inner cylinder which has a bottom face, The said inner cylinder Has a bottom surface and a side surface having a plurality of holes having a maximum diameter of 1 to 2 mm, and the inner cylinder can be arranged in the well casing with a side surface and a separation space of the well casing. Including tubes.

つぎに、本発明の浄化方法の例について図1及び2に基づき説明する。但し、本発明は以下の例に制限されない。   Next, an example of the purification method of the present invention will be described with reference to FIGS. However, the present invention is not limited to the following examples.

図1は、本発明の浄化方法の一実施形態を示す概略構成図である。図1において、栄養源供給井戸10は、汚染領域14内に形成されている。栄養源供給井戸10の孔は、地表面から表層1、不透水層2、透水層3の下部を超え不透水層4の内部に至る深さまで略垂直方向に採掘されている。栄養源供給井戸10の壁面には井戸ケーシング11が設けられ、その内部に内筒12が配置されている。井戸ケーシング11は、地下水が透過可能なスクリーン(ストレーナ)11aを備えている。スクリーン11aは、透水層3栄養源供給井戸10の底面から透水層3上部付近まで形成されている。内筒12は、井戸の底面及び井戸ケーシング11と離隔空間を保って井戸10内に配置されている。内筒12は、その内部に栄養源13が配置されている。内筒12は、側面及び底面に複数の孔を有するため、図中の矢印で示すように栄養源13を内筒の外に放出可能である。これにより、嫌気性微生物(例えば、Dehalococcoides属)を活性化し、嫌気性微生物による汚染物質の分解・浄化を促進できる。   FIG. 1 is a schematic configuration diagram showing an embodiment of the purification method of the present invention. In FIG. 1, the nutrient source supply well 10 is formed in the contaminated area 14. The holes of the nutrient supply well 10 are mined in a substantially vertical direction from the ground surface to a depth reaching the inside of the impermeable layer 4 beyond the surface layer 1, the impermeable layer 2, and the lower part of the permeable layer 3. A well casing 11 is provided on the wall surface of the nutrient source supply well 10, and an inner cylinder 12 is disposed therein. The well casing 11 includes a screen (strainer) 11a through which groundwater can pass. The screen 11 a is formed from the bottom surface of the water permeable layer 3 nutrient source supply well 10 to the vicinity of the upper part of the water permeable layer 3. The inner cylinder 12 is arranged in the well 10 while maintaining a space apart from the bottom of the well and the well casing 11. The inner cylinder 12 has a nutrient source 13 disposed therein. Since the inner cylinder 12 has a plurality of holes on the side surface and the bottom surface, the nutrient source 13 can be released to the outside of the inner cylinder as indicated by arrows in the figure. Thereby, anaerobic microorganisms (for example, Dehalococides genus) can be activated, and decomposition | disassembly and purification | cleaning of the contaminant by anaerobic microorganisms can be accelerated | stimulated.

図2は、1つの汚染領域14に複数の栄養源供給井戸10を形成した例を示す概略構成図である。図2中の矢印は地下水流の流れの方向を示す。図2において、汚染領域14を取り囲むように栄養源供給井戸10が14個形成され、さらに、汚染領域14内において特に汚染濃度が高い汚染領域24に栄養源供給井戸10が1つ形成されている。また、地下水流の下流側(図中右側)に位置する5つの栄養源供給井戸10は上流側に位置する栄養源供給井戸10よりも狭い間隔で形成されている。このように下流側の栄養源供給井戸10の間隔を狭くすることにより、これらの井戸が浄化壁として機能することができ、地下水の流れによる汚染物質の汚染領域14の外部への拡散を抑制できる。   FIG. 2 is a schematic configuration diagram showing an example in which a plurality of nutrient source supply wells 10 are formed in one contaminated area 14. The arrows in FIG. 2 indicate the direction of groundwater flow. In FIG. 2, 14 nutrient source supply wells 10 are formed so as to surround the contaminated region 14, and one nutrient source supply well 10 is formed in a contaminated region 24 having a particularly high contamination concentration in the contaminated region 14. . Further, the five nutrient source supply wells 10 located on the downstream side (right side in the figure) of the groundwater flow are formed at a narrower interval than the nutrient source supply wells 10 located on the upstream side. Thus, by narrowing the interval between the nutrient source supply wells 10 on the downstream side, these wells can function as purification walls, and the diffusion of contaminants to the outside of the contaminated region 14 due to the flow of groundwater can be suppressed. .

本発明は、汚染された土壌及び地下水の浄化に有用である。   The present invention is useful for the purification of contaminated soil and groundwater.

図1は、本発明の浄化方法の一例を示す概略構成図である。FIG. 1 is a schematic configuration diagram showing an example of the purification method of the present invention. 図2は、本発明の浄化方法のその他の例を示す概略構成図である。FIG. 2 is a schematic configuration diagram showing another example of the purification method of the present invention.

符号の説明Explanation of symbols

1・・・・表層
2・・・・不透水層
3・・・・透水層
4・・・・不透水層
10・・・栄養源供給井戸
11・・・井戸ケーシング
11a・・スクリーン
12・・・内筒
13・・・栄養源
14,24・・・汚染領域
DESCRIPTION OF SYMBOLS 1 ... Surface layer 2 ... Impervious layer 3 ... Impervious layer 4 ... Impervious layer 10 ... Nutrient source supply well 11 ... Well casing 11a ... Screen 12 ...・ Inner cylinder 13 ... Nutrient sources 14, 24 ... Contaminated area

Claims (4)

井戸ケーシング内に内筒が配置された栄養源供給井戸を形成すること、及び、
前記内筒に栄養源を注入することを含み、
前記栄養源は、ヘキシトール及びグリセリンを含み、前記栄養源の粘度(10℃)は、0.2Pa・S以上であり、
前記内筒は、最大径が0.5〜2.5mmである孔を複数備える側面及び底面を有し、かつ、前記井戸の底面及び前記井戸ケーシングの側面と離隔空間をもって配置されている、汚染土壌及び/又は地下水の浄化方法。
Forming a nutrient supply well in which an inner cylinder is arranged in a well casing; and
Injecting a nutrient source into the inner cylinder,
The nutrient source includes hexitol and glycerin, and the viscosity (10 ° C.) of the nutrient source is 0.2 Pa · S or more,
The inner cylinder has a side surface and a bottom surface including a plurality of holes having a maximum diameter of 0.5 to 2.5 mm, and is disposed with a space apart from the bottom surface of the well and the side surface of the well casing. A method for purifying soil and / or groundwater.
前記ヘキシトールが、ソルビトールである、請求項1に記載の浄化方法。 The purification method according to claim 1, wherein the hexitol is sorbitol. 前記栄養源供給井戸は、汚染領域を囲むように複数形成され、
地下水流の下流側における前記栄養源供給井戸の間隔は、地下水流の上流側における前記栄養源供給井戸の間隔よりも狭い、請求項1又は2記載の浄化方法。
A plurality of the nutrient source supply wells are formed so as to surround the contaminated area,
The purification method according to claim 1 or 2, wherein an interval between the nutrient source supply wells on the downstream side of the groundwater flow is narrower than an interval between the nutrient source supply wells on the upstream side of the groundwater flow.
前記栄養源供給井戸は、少なくとも透水層下部まで達している、請求項1から3のいずれか一項に記載の浄化方法。 The purification method according to any one of claims 1 to 3, wherein the nutrient source supply well reaches at least the bottom of the permeable layer.
JP2008132082A 2008-05-20 2008-05-20 Method of purifying contaminated soil and/or ground water Withdrawn JP2009279489A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI490334B (en) * 2013-03-29 2015-07-01 Panasonic Corp Microbial composition
CN108607878A (en) * 2018-04-28 2018-10-02 厦门理工学院 A kind of microorganism electrochemical method repairs the device and method of contaminated sites object
CN111922056A (en) * 2020-06-12 2020-11-13 生态环境部南京环境科学研究所 Chromium contaminated soil's heap leaching repair system
CN113617804A (en) * 2021-08-17 2021-11-09 昆明理工大学 Storage yard protection method based on sulfate reducing bacteria and biomass

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
TWI490334B (en) * 2013-03-29 2015-07-01 Panasonic Corp Microbial composition
CN108607878A (en) * 2018-04-28 2018-10-02 厦门理工学院 A kind of microorganism electrochemical method repairs the device and method of contaminated sites object
CN111922056A (en) * 2020-06-12 2020-11-13 生态环境部南京环境科学研究所 Chromium contaminated soil's heap leaching repair system
CN111922056B (en) * 2020-06-12 2021-12-21 生态环境部南京环境科学研究所 Chromium contaminated soil's heap leaching repair system
CN113617804A (en) * 2021-08-17 2021-11-09 昆明理工大学 Storage yard protection method based on sulfate reducing bacteria and biomass

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