JP4715059B2 - Method for decomposing organochlorine compounds in soil and / or groundwater - Google Patents

Method for decomposing organochlorine compounds in soil and / or groundwater Download PDF

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JP4715059B2
JP4715059B2 JP2001244029A JP2001244029A JP4715059B2 JP 4715059 B2 JP4715059 B2 JP 4715059B2 JP 2001244029 A JP2001244029 A JP 2001244029A JP 2001244029 A JP2001244029 A JP 2001244029A JP 4715059 B2 JP4715059 B2 JP 4715059B2
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soil
groundwater
growth substrate
treatment agent
compound
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JP2003053321A (en
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俊洋 上野
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Description

【0001】
【発明の属する技術分野】
本発明は、土壌及び/又は地下水中の有機塩素化合物を原位置にて分解処理する方法に関するものである。
【0002】
【従来の技術】
土壌や地下水は各種の有害難分解物質により汚染されることがある。中でもテトラクロロエチレン、トリクロロエチレン、ジクロロエチレン等の有機塩素化合物による汚染は深刻な問題となっている。
【0003】
有機塩素化合物等の汚染物質によって汚染された土壌及び/又は地下水を短期間で浄化する方法として、土壌及び/又は地下水中に汚染物質を分解するための処理剤を供給し、土壌及び/又は地下水中において汚染物質を分解する処理方法、いわゆる原位置処理法が新しい技術として注目されている。原位置処理法には微生物処理法があり、この微生物処理では、微生物の増殖基質を処理剤として土壌及び/又は地下水に供給し、土壌及び/又は地下水中に存在する微生物の作用により有機塩素化合物等の汚染物質を分解処理する。
【0004】
このような微生物処理法では、一般に塩素結合数の高い有機塩素化合物が、塩素結合数の少ない化合物に分解される。例えばテトラクロロエチレンは、順次トリクロロエチレン、ジクロロエチレン、塩化ビニルを経てエチレンに分解される。
【0005】
【発明が解決しようとする課題】
しかしながら、従来の微生物による原位置処理法では、テトラクロロエチレン及びトリクロロエチレン等の塩素結合数が3以上の化合物がジクロロエチレン等の塩素結合数2の化合物に分解されても、ジクロロエチレン等の塩素結合数2以下の有機塩素化合物が更に塩化ビニルやエチレンにまで分解されない場合があった。
【0006】
本発明は上記従来の問題点を解決し、微生物処理法により、土壌及び/又は地下水中の有機塩素化合物を分解処理する方法において、塩素結合数の少ない有機塩素化合物をも効率的に分解して無害化することができる土壌及び/又は地下水中の有機塩素化合物の分解方法を提供することを目的とする。
【0007】
【課題を解決するための手段】
本発明(請求項1)の土壌及び/又は地下水中の有機塩素化合物の分解方法は、微生物の増殖基質を土壌及び/又は地下水に供給し、該土壌及び/又は地下水中の有機塩素化合物を微生物の作用により分解処理する方法において、該増殖基質を、銀/塩化銀電極電位の酸化還元電位が−100〜−50Vの処理剤として、該土壌及び/又は地下水に供給する方法であって、該有機塩素化合物が、テトラクロロエチレン、トリクロロエチレン、ジクロロエチレン、塩化ビニル及びジクロロエタンよりなる群から選ばれる1種又は2種以上の物質であり、該土壌中の有機塩素化合物含有量が0.05〜5mg/kgで、該地下水中の有機塩素化合物含有量が0.1〜10mg/Lであり、該増殖基質がクエン酸及び/又はクエン酸塩であり、該処理剤中の増殖基質の含有量が10〜1000mg/Lであり、該増殖基質を含む液を、金属鉄及び/又は硫化鉄を充填したカラムに通水することにより金属鉄及び/又は硫化鉄に接触させることにより調製した該処理剤を、該土壌及び/又は地下水に供給することにより、該土壌及び/又は地下水中の塩素結合数2以下の有機塩素化合物を塩化ビニル又はエチレンに分解処理することを特徴とする。
【0008】
本発明(請求項2)の土壌及び/又は地下水中の有機塩素化合物の分解方法は、微生物の増殖基質を土壌及び/又は地下水に供給し、該土壌及び/又は地下水中の有機塩素化合物を微生物の作用により分解処理する方法において、該増殖基質を、銀/塩化銀電極電位の酸化還元電位が−100〜−50mVの処理剤として、該土壌及び/又は地下水に供給する方法であって、該有機塩素化合物が、テトラクロロエチレン、トリクロロエチレン、ジクロロエチレン、塩化ビニル及びジクロロエタンよりなる群から選ばれる1種又は2種以上の物質であり、該土壌中の有機塩素化合物含有量が0.05〜5mg/kgで、該地下水中の有機塩素化合物含有量が0.1〜10mg/Lであり、該増殖基質がクエン酸及び/又はクエン酸塩であり、該処理剤中の増殖基質の含有量が10〜1000mg/Lであり、金属鉄及び/又は硫化鉄を充填したカラムに通水することにより金属鉄及び/又は硫化鉄に接触させた水と増殖基質とを混合することにより調製した該処理剤を、該土壌及び/又は地下水に供給することにより、該土壌及び/又は地下水中の塩素結合数2以下の有機塩素化合物を塩化ビニル又はエチレンに分解処理することを特徴とする。
【0009】
有機塩素化合物は増殖基質の存在下、微生物の作用によって分解される。この分解反応は嫌気条件下において進行し、例えば、テトラクロロエチレンはトリクロロエチレン、ジクロロエチレン、塩化ビニルを経てエチレンに分解される。また、ジクロロエチレンは直接エチレンに分解される。しかしながら、従来の微生物処理法では、テトラクロロエチレン、トリクロロエチレン等の塩素結合数3以上の有機塩素化合物はジクロロエチレン等の塩素結合数2以下の化合物に分解されるのに対して、ジクロロエチレン等の塩素結合数2以下の有機塩素化合物は分解されない場合があった。
【0010】
本発明者は、この原因について検討したところ、酸化還元電位が+100mV以上の条件に微生物を晒すと、上述のような現象が起こることを確認した。即ち、微生物処理法において増殖基質を土壌及び/又は地下水に供給する場合、増殖基質を水で溶解ないし希釈して土壌及び/又は地下水に注入するが、この増殖基質溶液の酸化還元電位が高いと土壌及び/又は地下水の酸化還元電位も高くなり、上記の現象が生じ、塩素結合数2以下の有機塩素化合物は分解されずに土壌及び/又は地下水に残留することとなる。
【0011】
本発明では、増殖基質を銀/塩化銀電極電位の酸化還元電位(以下、単に「ORP」と記す。)が−100〜−50Vの処理剤として土壌及び/又は地下水に注入するため、上記現象は防止され、ジクロロエチレン等の塩素結合数2以下の有機塩素化合物をも確実に分解処理することが可能となる
【0012】
【発明の実施の形態】
下に本発明の土壌及び/又は地下水中の有機塩素化合物の分解方法の実施の形態を詳細に説明する。
【0013】
本発明において、処理対象となる有機塩素化合物は、土壌及び/又は地下水に含まれる有機塩素化合物であり、その種類としては微生物処理によって分解、除去できるものであ、テトラクロロエチレン(PCE)、トリクロロエチレン(TCE)、ジクロロエチレン(DCE)、塩化ビニル(VC)、ジクロロエタン(DCA)の有機塩素化合物が処理対象として適している。土壌及び/又は地下水中には、これらの有機塩素化合物の1種が単独で含まれていても良く、2種類以上が複合して含まれていても良い。
【0014】
土壌及び/又は地下水中のこれらの有機塩素化合物の含有量、土壌では0.05〜5mg/kg、地下水では0.1〜10mg/Lが処理に適している。
【0015】
このような有機塩素化合物の処理に使用する処理剤の有効成分となる微生物の増殖基質としては、微生物を用いる原位置処理により上記有機塩素化合物を分解除去できる増殖基質であ、クエン酸或いはこのナトリウム塩、カリウム塩、カルシウム塩、マグネシウム塩、鉄塩等の塩である。これらの増殖基質は、処理剤中に1種が単独で含まれていても2種以上が混合されて含まれていても良い。
【0016】
これらの増殖基質のうち、鉄などの金属イオンに対してキレート能を有するので、金属イオンの沈殿を防止することができること、および中性付近でのpH緩衝能を有すること等の点で、特に、クエン酸或いはそのナトリウム塩、カリウム塩等が好ましい。
【0017】
本発明で用いる処理剤中の増殖基質の好適な含有量は、10〜1000mg/L、好ましくは50〜300mg/Lであ、処理剤はこのような濃度の増殖基質水溶液として調製される。
【0018】
なお、本発明における微生物処理では、土壌及び/又は地下水中に存在する微生物を利用して処理を行うため、特に微生物を供給する必要はないが、有機塩素化合物の分解活性の高い微生物を、処理剤中に含有させて供給しても良く、或いは処理剤とは別に土壌及び/又は地下水に供給して接種して処理を行っても良い。
【0019】
本発明では、前記増殖基質を含有し、ORPが−50mV以下の処理剤を使用する。処理剤のORPが+100mVよりも高いと、土壌及び/又は地下水のORPを上昇させ、塩素結合数2以下の有機塩素化合物を分解し得なくなる。
【0020】
このため、本発明では、増殖基質を溶解又は希釈して得た増殖基質溶液を還元処理するか、或いは還元処理した水を用いて増殖基質を溶解又は希釈することにより、ORP−50mV以下の増殖基質含有処理剤を調製する。
【0021】
この還元処理は、例えば、増殖基質溶液或いは増殖基質の溶解又は希釈水を金属鉄及び/又は硫化鉄と接触させることにより行うことができる。ここで用いる金属鉄や硫化鉄は表面積の大きいものが望ましく、多孔質に成形したものやファイバー状に成形したものが使用できる。接触方法は、カラム通水法であり、接触時間は10〜20分程度とすることができる。このような還元処理によれば、ORP+100mV〜−100mV程度の処理剤を調製することができる。
【0022】
本発明の方法では、このようにしてORPを調製した増殖基質含有処理剤を、土壌及び/又は地下水に供給して土壌及び/又は地下水中に拡散させ、土壌及び/又は地下水中の微生物を増殖させて、微生物の作用を利用して土壌及び/又は地下水中の有機塩素化合物を分解処理する。
【0023】
土壌及び/又は地下水に処理剤を供給する方法は、土壌中に設置した井戸や浸透桝等の処理剤供給設備により処理剤を土壌及び/又は地下水に供給する方法、処理剤を土壌表層部に供給して深層部に処理剤を沈降拡散させる方法等を採用することができる。
【0024】
このようにして、土壌及び/又は地下水中に供給された処理剤は、土壌及び/又は地下水中に拡散し、土壌及び/又は地下水中に含まれる有機塩素化合物は微生物反応により分解されて無害化される。この場合、PCE、TCE等の塩素結合数3以上の有機塩素化合物はDCE、VC等の塩素結合数2以下の有機塩素化合物を経て分解されるが、本発明ではORPが−100〜−50Vの処理剤を用いることにより、塩素結合数2以下の有機塩素化合物をも効率的に分解することが可能になり、土壌及び/又は地下水中のこれらの有機塩素化合物の残留を防止して、土壌及び/又は地下水を確実に浄化することができる。
【0025】
【実施例】
以下に実施例及び比較例を挙げて本発明をより具体的に説明するが、本発明はその要旨を超えない限り、以下の実施例に限定されるものではない。
【0026】
実施例1
水道水に、増殖基質としてクエン酸ナトリウムを500mg/Lとなるように加えて増殖基質水溶液とした。この増殖基質水溶液のORPは+300mVであった。この増殖基質水溶液を金属鉄を充填したカラムに通水することによって還元処理を行い、ORPを−50mVの増殖基質含有処理剤とした。カラム内の水滞留時間は10分とした。
【0027】
この増殖基質含有処理剤100mLをバイアル瓶にいれ、PCE、TCE、DCE、VC及びDCAで汚染された土壌50mLを添加して密栓し、30℃で培養した。
【0028】
ヘッドスペースガスをガスクロマトグラフィーで分析することにより、有機塩素化合物濃度の変化を調べ、結果を図1に示した。
【0029】
実施例2
実施例1において、金属鉄充填カラムの代わりに硫化鉄充填カラムを用いたこと以外は同様にして実験を行い、結果を図2に示した。なお、硫化鉄充填カラムでの還元処理後の増殖基質含有処理剤のORPは−100mVであった。
【0030】
比較例1
実施例1において、還元処理を行わず、ORP+300mVの増殖基質水溶液を用いたこと以外は同様にして実験を行い、結果を図3に示した。
【0031】
図1〜3より次のことが明らかである。
【0032】
即ち、ORP+300mVの増殖基質水溶液を用いた比較例1では、PCE、TCEは分解されたものの、DCE(cis−DCE)が生成し、このDCEの塩化ビニル(VC)やエチレンへの分解反応が起こらず、DCEが残留した。また、DCAの分解反応も起こらなかった。このため、有機塩素化合物を完全に分解除去することができなかった。
【0033】
これに対して、ORP−50mVの増殖基質含有処理剤を用いた実施例1及びORP−100mVの増殖基質含有処理剤を用いた実施例2では、すべての有機塩素化合物が分解されてエチレンに変換された。
【0034】
これらの結果から、増殖基質溶液を還元処理してORPを低下させることにより、有機塩素化合物を効率的に分解し、塩素結合数2以下の有機塩素化合物の残留を防止することができることがわかる。
【0035】
【発明の効果】
以上の通り、本発明の土壌及び/又は地下水中の有機塩素化合物の分解方法によれば、ORP−100〜−50Vの増殖基質含有処理剤を供給することにより、塩素結合数の多い有機塩素化合物のみならず、塩素結合数の少ない有機塩素化合物をも効率的に分解して無害化することができるため、これらの有機塩素化合物の残留を防止して、土壌及び/又は地下水を確実に浄化することができる。
【図面の簡単な説明】
【図1】 実施例1の結果を示すグラフである。
【図2】 実施例2の結果を示すグラフである。
【図3】 比較例1の結果を示すグラフである。
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method for decomposing organochlorine compounds in soil and / or groundwater in situ.
[0002]
[Prior art]
Soil and groundwater can be polluted by various harmful persistent substances. In particular, contamination with organic chlorine compounds such as tetrachloroethylene, trichlorethylene, and dichloroethylene is a serious problem.
[0003]
As a method for purifying soil and / or groundwater contaminated with pollutants such as organochlorine compounds in a short period of time, a treatment agent for decomposing the pollutants is supplied to the soil and / or groundwater, and the soil and / or groundwater Among them, a processing method for decomposing contaminants, a so-called in-situ processing method, has attracted attention as a new technology. The in-situ treatment method includes a microbial treatment method. In this microbial treatment, a microbial growth substrate is supplied as a treatment agent to soil and / or groundwater, and an organochlorine compound is produced by the action of microorganisms present in the soil and / or groundwater. Decompose contaminants such as
[0004]
In such a microbial treatment method, an organic chlorine compound having a high chlorine bond number is generally decomposed into a compound having a low chlorine bond number. For example, tetrachlorethylene is sequentially decomposed into ethylene via trichlorethylene, dichloroethylene, and vinyl chloride.
[0005]
[Problems to be solved by the invention]
However, in the conventional in-situ treatment method using microorganisms, even if a compound having 3 or more chlorine bonds such as tetrachloroethylene and trichlorethylene is decomposed into a compound having 2 chlorine bonds such as dichloroethylene, the number of chlorine bonds such as dichloroethylene is 2 or less. In some cases, the organic chlorine compound was not further decomposed into vinyl chloride or ethylene.
[0006]
The present invention solves the above-mentioned conventional problems, and in a method for decomposing organochlorine compounds in soil and / or groundwater by a microbial treatment method, an organochlorine compound having a small number of chlorine bonds is efficiently decomposed. It is an object of the present invention to provide a method for decomposing organochlorine compounds in soil and / or groundwater that can be rendered harmless.
[0007]
[Means for Solving the Problems]
The method for decomposing organochlorine compounds in soil and / or groundwater of the present invention (Claim 1) supplies a growth substrate of microorganisms to the soil and / or groundwater, and the organochlorine compounds in the soil and / or groundwater are transformed into microorganisms. a method of decomposing by the action, the growth substrates, as a processing agent for a silver / redox potential of the silver chloride electrode potential -100 to-50 m V, a method of supplying to the soil and / or groundwater The organic chlorine compound is one or more substances selected from the group consisting of tetrachloroethylene, trichloroethylene, dichloroethylene, vinyl chloride and dichloroethane, and the organic chlorine compound content in the soil is 0.05 to 5 mg / kg, the content of organochlorine compound in the groundwater is 0.1 to 10 mg / L, and the growth substrate is citric acid and / or citrate, The content of the growth substrate in the treatment agent is 10 to 1000 mg / L, and the liquid containing the growth substrate is passed through a column filled with metal iron and / or iron sulfide to cause metal iron and / or iron sulfide. By supplying the treating agent prepared by contacting to the soil and / or groundwater, the organochlorine compound having 2 or less chlorine bonds in the soil and / or groundwater is decomposed into vinyl chloride or ethylene. It is characterized by that.
[0008]
In the method for decomposing organochlorine compounds in soil and / or groundwater according to the present invention (claim 2), a microorganism growth substrate is supplied to the soil and / or groundwater, and the organochlorine compounds in the soil and / or groundwater are converted into microorganisms. A method for supplying the growth substrate to the soil and / or groundwater as a treatment agent having a redox potential of a silver / silver chloride electrode potential of −100 to −50 mV, The organochlorine compound is one or more substances selected from the group consisting of tetrachloroethylene, trichloroethylene, dichloroethylene, vinyl chloride and dichloroethane, and the organochlorine compound content in the soil is 0.05 to 5 mg / kg. The organochlorine compound content in the groundwater is 0.1 to 10 mg / L, the growth substrate is citric acid and / or citrate, The growth substrate content in the agent is 10 to 1000 mg / L, and the water and the growth substrate are brought into contact with the metal iron and / or iron sulfide by passing water through a column filled with metal iron and / or iron sulfide. By supplying the treating agent prepared by mixing to the soil and / or groundwater, the organic chlorine compound having a chlorine bond number of 2 or less in the soil and / or groundwater is decomposed into vinyl chloride or ethylene. It is characterized by doing.
[0009]
Organochlorine compounds are degraded by the action of microorganisms in the presence of growth substrates. This decomposition reaction proceeds under anaerobic conditions. For example, tetrachloroethylene is decomposed into ethylene via trichlorethylene, dichloroethylene, and vinyl chloride. In addition, dichloroethylene is directly decomposed into ethylene. However, in the conventional microbial treatment method, an organic chlorine compound having 3 or more chlorine bonds such as tetrachloroethylene or trichloroethylene is decomposed into a compound having 2 or less chlorine bonds such as dichloroethylene, whereas the number of chlorine bonds such as dichloroethylene is 2 The following organochlorine compounds may not be decomposed.
[0010]
The present inventor examined this cause and confirmed that the above-described phenomenon occurs when the microorganism is exposed to a condition where the oxidation-reduction potential is +100 mV or more. That is, when supplying the growth substrate to soil and / or groundwater in the microbial treatment method, the growth substrate is dissolved or diluted with water and injected into the soil and / or groundwater. If the growth substrate solution has a high redox potential, The oxidation-reduction potential of soil and / or groundwater also increases, the above phenomenon occurs, and the organic chlorine compound having a chlorine bond number of 2 or less remains in the soil and / or groundwater without being decomposed.
[0011]
In the present invention, the growth substrate is injected into soil and / or groundwater as a treatment agent having a redox potential of the silver / silver chloride electrode potential (hereinafter simply referred to as “ORP”) of −100 to −50 mV , The above phenomenon is prevented, and an organic chlorine compound having a chlorine bond number of 2 or less such as dichloroethylene can be reliably decomposed .
[0012]
DETAILED DESCRIPTION OF THE INVENTION
An embodiment of the method for decomposing soil and / or organic chlorine compounds in the groundwater of the present invention will be described in detail below.
[0013]
In the present invention, an organic chlorine compound to be processed is an organic chlorine compounds contained in soil and / or groundwater, degraded by microbial treatment as the type state, and are not capable of removing, tetrachlorethylene (PCE), trichlorethylene ( Organochlorine compounds such as TCE), dichloroethylene (DCE), vinyl chloride (VC), and dichloroethane (DCA ) are suitable as treatment targets. One kind of these organic chlorine compounds may be contained alone or two or more kinds may be contained in combination in the soil and / or groundwater.
[0014]
The content of these organic chlorine compounds in soil and / or groundwater, in the soil 0.05 to 5 mg / kg, in the ground water 0.1 to 10 mg / L is suitable for processing.
[0015]
The growth substrate of microorganisms comprising as an active ingredient of the treatment agent used in the treatment of the organic chlorine compounds, Ri growth substrates der capable decompose and remove the organic chlorine compounds by situ process using microorganisms, some have citrate the sodium salt, potassium salt, calcium salt, magnesium salt, a salt such as an iron salt. These growth substrates may be contained alone or in a combination of two or more in the treatment agent.
[0016]
Among these growth substrates, since it has a chelating ability for metal ions such as iron, it can prevent precipitation of metal ions and has a pH buffering ability in the vicinity of neutrality. Citric acid or its sodium salt or potassium salt is preferred.
[0017]
Suitable content of the growth substrate in the treatment agent used in the present invention, 1 0~1000mg / L, is prepared preferably Ri 50 to 300 mg / L der, treating agent as a growth substrate an aqueous solution of such concentration .
[0018]
In the microorganism treatment according to the present invention, since the treatment is performed using microorganisms present in soil and / or groundwater, it is not particularly necessary to supply microorganisms, but microorganisms having a high organochlorine compound decomposition activity are treated. It may be supplied by being contained in the agent, or may be treated by inoculating it by supplying it to soil and / or groundwater separately from the treatment agent.
[0019]
In the present invention, a treatment agent containing the growth substrate and having an ORP of −50 mV or less is used. When the ORP of the treatment agent is higher than +100 mV, the ORP of the soil and / or groundwater is increased, and the organic chlorine compound having a chlorine bond number of 2 or less cannot be decomposed.
[0020]
For this reason, in the present invention, the growth substrate solution obtained by dissolving or diluting the growth substrate is reduced, or the growth substrate is dissolved or diluted with reduced water, so that the OR P- 50 mV or less. A growth substrate-containing treatment agent is prepared.
[0021]
This reduction treatment can be performed, for example, by bringing a growth substrate solution or a growth substrate solution or diluted water into contact with metallic iron and / or iron sulfide. The metal iron or iron sulfide used here preferably has a large surface area, and can be formed into a porous shape or a fiber shape. The contact method is a column flow method , and the contact time can be about 10 to 20 minutes. According to such a reduction treatment, a treatment agent of about ORP + 100 mV to −100 mV can be prepared.
[0022]
In the method of the present invention, the growth substrate-containing treatment agent prepared as described above is supplied to the soil and / or groundwater and diffused in the soil and / or groundwater, and the microorganisms in the soil and / or groundwater are propagated. Then, the organochlorine compound in the soil and / or groundwater is decomposed using the action of microorganisms.
[0023]
The method of supplying the treatment agent to the soil and / or groundwater is a method of supplying the treatment agent to the soil and / or groundwater by a treatment agent supply facility such as a well or a seepage pit installed in the soil, and the treatment agent to the surface layer of the soil. For example, a method of supplying and allowing the treatment agent to settle and diffuse in the deep layer can be employed.
[0024]
In this way, the treatment agent supplied to the soil and / or groundwater diffuses into the soil and / or groundwater, and the organic chlorine compound contained in the soil and / or groundwater is decomposed and rendered harmless by the microbial reaction. Is done. In this case, organochlorine compounds having 3 or more chlorine bonds such as PCE and TCE are decomposed via organochlorine compounds having 2 or less chlorine bonds such as DCE and VC. In the present invention, ORP is −100 to −50 m. By using the treating agent of V, it becomes possible to efficiently decompose an organic chlorine compound having a chlorine bond number of 2 or less, preventing the residue of these organic chlorine compounds in soil and / or groundwater, Soil and / or groundwater can be reliably purified.
[0025]
【Example】
Hereinafter, the present invention will be described more specifically with reference to examples and comparative examples. However, the present invention is not limited to the following examples as long as the gist thereof is not exceeded.
[0026]
Example 1
To the tap water, sodium citrate was added as a growth substrate at 500 mg / L to obtain a growth substrate aqueous solution. The ORP of this aqueous growth substrate solution was +300 mV. The reduction treatment was carried out by passing the aqueous growth substrate solution through a column filled with metallic iron, and ORP was used as a growth substrate-containing treatment agent of −50 mV. The water residence time in the column was 10 minutes.
[0027]
100 mL of this growth substrate-containing treatment agent was placed in a vial, 50 mL of soil contaminated with PCE, TCE, DCE, VC and DCA was added, sealed, and cultured at 30 ° C.
[0028]
The headspace gas was analyzed by gas chromatography to examine changes in the organochlorine compound concentration, and the results are shown in FIG.
[0029]
Example 2
In Example 1, an experiment was performed in the same manner except that an iron sulfide packed column was used instead of the metal iron packed column, and the result is shown in FIG. The ORP of the growth substrate-containing treatment agent after the reduction treatment in the iron sulfide-filled column was −100 mV.
[0030]
Comparative Example 1
In Example 1, an experiment was performed in the same manner except that the reduction treatment was not performed and an ORP + 300 mV growth substrate aqueous solution was used, and the results are shown in FIG.
[0031]
The following is clear from FIGS.
[0032]
That is, in Comparative Example 1 using an ORP + 300 mV growth substrate aqueous solution, although PCE and TCE were decomposed, DCE (cis-DCE) was produced, and this DCE was decomposed into vinyl chloride (VC) or ethylene. However, DCE remained. In addition, the decomposition reaction of DCA did not occur. For this reason, the organochlorine compound could not be completely decomposed and removed.
[0033]
In contrast, in Example 1 using the ORP-50 mV growth substrate-containing treatment agent and Example 2 using the ORP-100 mV growth substrate-containing treatment agent, all organochlorine compounds were decomposed and converted to ethylene. It was done.
[0034]
From these results, it can be seen that by reducing the ORP by reducing the growth substrate solution, the organic chlorine compound can be efficiently decomposed and the residual organic chlorine compound having 2 or less chlorine bonds can be prevented.
[0035]
【The invention's effect】
As described above, according to the method for decomposing organochlorine compounds in the soil and / or groundwater of the present invention, by supplying the growth substrate-containing treatment agent of ORP -100 to -50 mV , the organic compound having a large number of chlorine bonds. Since not only chlorine compounds but also organic chlorine compounds with a small number of chlorine bonds can be efficiently decomposed and detoxified, the residue of these organic chlorine compounds can be prevented to ensure soil and / or groundwater Can be purified.
[Brief description of the drawings]
1 is a graph showing the results of Example 1. FIG.
2 is a graph showing the results of Example 2. FIG.
3 is a graph showing the results of Comparative Example 1. FIG.

Claims (2)

微生物の増殖基質を土壌及び/又は地下水に供給し、該土壌及び/又は地下水中の有機塩素化合物を微生物の作用により分解処理する方法において、
該増殖基質を、銀/塩化銀電極電位の酸化還元電位が−100〜−50Vの処理剤として、該土壌及び/又は地下水に供給する方法であって、
該有機塩素化合物が、テトラクロロエチレン、トリクロロエチレン、ジクロロエチレン、塩化ビニル及びジクロロエタンよりなる群から選ばれる1種又は2種以上の物質であり、
該土壌中の有機塩素化合物含有量が0.05〜5mg/kgで、該地下水中の有機塩素化合物含有量が0.1〜10mg/Lであり、
該増殖基質がクエン酸及び/又はクエン酸塩であり、該処理剤中の増殖基質の含有量が10〜1000mg/Lであり、
該増殖基質を含む液を、金属鉄及び/又は硫化鉄を充填したカラムに通水することにより金属鉄及び/又は硫化鉄に接触させることにより調製した該処理剤を、該土壌及び/又は地下水に供給することにより、該土壌及び/又は地下水中の塩素結合数2以下の有機塩素化合物を塩化ビニル又はエチレンに分解処理することを特徴とする土壌及び/又は地下水中の有機塩素化合物の分解方法。
In a method of supplying a growth substrate of microorganisms to soil and / or groundwater and decomposing an organic chlorine compound in the soil and / or groundwater by the action of microorganisms,
A method of supplying the growth substrate to the soil and / or groundwater as a treatment agent having a redox potential of a silver / silver chloride electrode potential of −100 to −50 mV ,
The organochlorine compound is one or more substances selected from the group consisting of tetrachloroethylene, trichloroethylene, dichloroethylene, vinyl chloride and dichloroethane;
The organochlorine compound content in the soil is 0.05 to 5 mg / kg, the organochlorine compound content in the groundwater is 0.1 to 10 mg / L,
The growth substrate is citric acid and / or citrate, and the content of the growth substrate in the treatment agent is 10 to 1000 mg / L,
The treatment agent prepared by bringing the liquid containing the growth substrate into contact with metal iron and / or iron sulfide by passing water through a column filled with metal iron and / or iron sulfide is used as the soil and / or groundwater. The organic chlorine compound having a chlorine bond number of 2 or less in the soil and / or ground water is decomposed into vinyl chloride or ethylene by supplying to the soil and / or ground water, and the organic chlorine compound in the soil and / or ground water is decomposed .
微生物の増殖基質を土壌及び/又は地下水に供給し、該土壌及び/又は地下水中の有機塩素化合物を微生物の作用により分解処理する方法において、
該増殖基質を、銀/塩化銀電極電位の酸化還元電位が−100〜−50Vの処理剤として、該土壌及び/又は地下水に供給する方法であって、
該有機塩素化合物が、テトラクロロエチレン、トリクロロエチレン、ジクロロエチレン、塩化ビニル及びジクロロエタンよりなる群から選ばれる1種又は2種以上の物質であり、
該土壌中の有機塩素化合物含有量が0.05〜5mg/kgで、該地下水中の有機塩素化合物含有量が0.1〜10mg/Lであり、
該増殖基質がクエン酸及び/又はクエン酸塩であり、該処理剤中の増殖基質の含有量が10〜1000mg/Lであり、
金属鉄及び/又は硫化鉄を充填したカラムに通水することにより金属鉄及び/又は硫化鉄に接触させた水と増殖基質とを混合することにより調製した該処理剤を、該土壌及び/又は地下水に供給することにより、該土壌及び/又は地下水中の塩素結合数2以下の有機塩素化合物を塩化ビニル又はエチレンに分解処理することを特徴とする土壌及び/又は地下水中の有機塩素化合物の分解方法。
In a method of supplying a growth substrate of microorganisms to soil and / or groundwater and decomposing an organic chlorine compound in the soil and / or groundwater by the action of microorganisms,
A method of supplying the growth substrate to the soil and / or groundwater as a treatment agent having a redox potential of a silver / silver chloride electrode potential of −100 to −50 mV ,
The organochlorine compound is one or more substances selected from the group consisting of tetrachloroethylene, trichloroethylene, dichloroethylene, vinyl chloride and dichloroethane;
The organochlorine compound content in the soil is 0.05 to 5 mg / kg, the organochlorine compound content in the groundwater is 0.1 to 10 mg / L,
The growth substrate is citric acid and / or citrate, and the content of the growth substrate in the treatment agent is 10 to 1000 mg / L,
The treatment agent prepared by mixing water and a growth substrate in contact with metallic iron and / or iron sulfide by passing water through a column filled with metallic iron and / or iron sulfide, and the soil and / or Decomposing organochlorine compounds in soil and / or groundwater by decomposing organochlorine compounds having 2 or less chlorine bonds in the soil and / or groundwater into vinyl chloride or ethylene by supplying to groundwater Method.
JP2001244029A 2001-08-10 2001-08-10 Method for decomposing organochlorine compounds in soil and / or groundwater Expired - Fee Related JP4715059B2 (en)

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