JP2008029935A - Method for arranging cleaning agent in contaminated soil, and method for cleaning contaminated soil and/or ground water in situ - Google Patents
Method for arranging cleaning agent in contaminated soil, and method for cleaning contaminated soil and/or ground water in situ Download PDFInfo
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- JP2008029935A JP2008029935A JP2006204887A JP2006204887A JP2008029935A JP 2008029935 A JP2008029935 A JP 2008029935A JP 2006204887 A JP2006204887 A JP 2006204887A JP 2006204887 A JP2006204887 A JP 2006204887A JP 2008029935 A JP2008029935 A JP 2008029935A
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- 239000002689 soil Substances 0.000 title claims abstract description 29
- 238000000034 method Methods 0.000 title claims abstract description 28
- 239000003673 groundwater Substances 0.000 title claims abstract description 25
- 238000011065 in-situ storage Methods 0.000 title claims abstract description 10
- 239000012459 cleaning agent Substances 0.000 title abstract description 13
- 238000004140 cleaning Methods 0.000 title abstract 2
- 238000000746 purification Methods 0.000 claims description 60
- 239000003795 chemical substances by application Substances 0.000 claims description 42
- 238000009412 basement excavation Methods 0.000 claims description 32
- 239000008187 granular material Substances 0.000 claims description 17
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 abstract description 22
- 239000004576 sand Substances 0.000 abstract description 19
- 238000005325 percolation Methods 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 19
- 229910052751 metal Inorganic materials 0.000 description 11
- 239000002184 metal Substances 0.000 description 11
- 239000000843 powder Substances 0.000 description 11
- 239000012629 purifying agent Substances 0.000 description 8
- 239000006185 dispersion Substances 0.000 description 4
- 238000005553 drilling Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 2
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 229910052801 chlorine Inorganic materials 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 229910052731 fluorine Inorganic materials 0.000 description 2
- 239000011737 fluorine Substances 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 150000004045 organic chlorine compounds Chemical class 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 150000002505 iron Chemical class 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
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- Removal Of Specific Substances (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Description
本発明は、化学物質によって汚染された土壌及び/又は地下水を原位置において浄化剤によって浄化する技術に関する。 The present invention relates to a technique for purifying soil and / or groundwater contaminated with a chemical substance with a purifier in situ.
有機塩素系化合物によって汚染された土壌及び地下水を原位置において浄化する方法としては、例えば特開平10−71386号や特開平10−263522号のように、汚染土壌中の所定位置に有機塩素系化合物を浄化するための金属鉄粉の分散層を形成する方法が知られている。このような浄化剤分散層を形成する方法としては、ケーシング掘削法、開削法、泥水掘削法などが利用されている。 As a method for purifying soil and groundwater contaminated with an organic chlorine-based compound in situ, for example, as disclosed in JP-A-10-71386 and JP-A-10-263522, an organic chlorine-based compound is placed at a predetermined position in the contaminated soil. There is known a method of forming a dispersed layer of metallic iron powder for purifying the metal. As a method for forming such a purifier dispersion layer, a casing excavation method, an open-cut method, a mud excavation method, and the like are used.
このような浄化剤の分散層を形成するとき、浄化用金属粉を単独で用いる場合もあるが、浄化用金属粉と透水用粒状物とを混合して混合浄化剤として用いる場合もある。この透水用粒状物は充填された状態での透水性を確保するためや、現場ごとに求められる浄化能力によって浄化用金属粉の添加量を調整するために用いられる。 When such a purification agent dispersion layer is formed, the purification metal powder may be used alone, or the purification metal powder and the water-permeable granular material may be mixed and used as a mixed purification agent. This water-permeable granular material is used to ensure water permeability in a filled state, or to adjust the amount of metal powder for purification that is added depending on the purification capacity required for each site.
透水用粒状物を用いる場合、地中に分散層を形成したときに分散層のどの部位においても浄化用金属粉と透水用粒状物との混合比がムラなく一定範囲になっている必要がある。これは、混合ムラがあると、汚染土壌、汚染地下水の浄化が効率良く行われず、結果的に浄化期間が延びてしまうからである。 When using the water-permeable granular material, the mixing ratio of the metal powder for purification and the water-permeable granular material must be within a certain range in any part of the dispersion layer when the dispersion layer is formed in the ground. . This is because if there is uneven mixing, the contaminated soil and contaminated groundwater cannot be efficiently purified, resulting in an extended purification period.
しかし浄化用金属粉と透水用粒状物とは形状が大きく異なることがあり、その場合、混合して充填する施工中に浄化用金属粉と透水用粒状物との混合にムラが生じてしまうという問題がある。特に地下水位より深く掘削部、例えばボーリング孔を設け、該掘削部内に地上から浄化用金属粉と透水用粒状物との混合物からなる浄化剤を注入する場合、掘削部内に溜った水(地下水)中を該混合物が沈降するときに、金属粉と透水用粒状物との比重差により両者が分離してしまい、混合に大きなムラが生じてしまう。
本発明は、上記従来技術の問題点を解決し、汚染土壌に設けた掘削部の最深部に浄化剤と透水用粒状物との混合浄化剤を混合ムラなく配置することができる浄化剤配置方法と汚染土壌及び/又は地下水の原位置浄化方法とを提供することを目的とする。 The present invention solves the above-mentioned problems of the prior art, and a purification agent arrangement method capable of arranging a mixed purification agent of a purification agent and a water-permeable granular material in the deepest part of an excavation part provided in contaminated soil without mixing unevenness. And an in-situ purification method for contaminated soil and / or groundwater.
本発明の浄化剤配置方法は、土壌の掘削部の最深部に浄化剤と透水用粒状物とを含む混合浄化剤を配置する方法であって、底部が開閉可能な容器内に該混合浄化剤を収容し、該容器を掘削部の最深部に下ろし、次いで該容器の底部を開放して混合浄化剤を放出させることにより、該掘削部内に該混合浄化剤を配置することを特徴とするものである。 The purification agent disposing method of the present invention is a method of disposing a mixed purifying agent containing a purifying agent and water-permeable granular material at the deepest part of a soil excavation part, wherein the mixed purifying agent is placed in a container whose bottom can be opened and closed. The mixed purifier is disposed in the excavation part by lowering the container to the deepest part of the excavation part and then releasing the mixed purifier by opening the bottom of the container. It is.
本発明の汚染土壌及び/又は地下水の原位置浄化方法は、汚染土壌に掘削部を設け、この掘削部の最深部に浄化剤と透水用粒状物とを含む混合浄化剤を配置し、該混合浄化剤によって土壌及び/又は地下水の浄化を行う汚染土壌及び/又は地下水の原位置浄化方法であって、底部が開閉可能な容器内に該混合浄化剤を収容し、該容器を掘削部の最深部に下ろし、次いで該容器の底部を開放して混合浄化剤を放出させることにより、該掘削部内に該混合浄化剤を配置することを特徴とするものである。 In the in-situ purification method for contaminated soil and / or groundwater of the present invention, an excavation part is provided in the contaminated soil, and a mixed purification agent containing a purification agent and water-permeable granular material is disposed at the deepest part of the excavation part, and the mixing A method for in-situ purification of contaminated soil and / or groundwater that purifies soil and / or groundwater with a purifier, wherein the mixed purifier is contained in a container whose bottom can be opened and closed, and the container is placed at the deepest of the excavation part. The mixed cleaning agent is disposed in the excavation part by lowering the container to the bottom and then releasing the mixed cleaning agent by opening the bottom of the container.
本発明では、浄化剤と透水用粒状物との混合浄化剤を容器に収容して掘削部の最深部に下ろし、次いで容器底部を開放させて容器から混合浄化剤を該最深部に放出する。従って、掘削部が地下水位よりも深く設けてある場合であっても、混合浄化剤が掘削部内の水中を沈降落下することがなく、この沈降落下に起因した混合浄化剤の分離現象が防止される。これにより、汚染土壌及び/又は地下水を効率よく浄化することが可能となる。 In the present invention, the mixed purification agent of the purification agent and the water-permeable granular material is accommodated in the container and lowered to the deepest part of the excavation part, and then the bottom of the container is opened to release the mixed purification agent from the container to the deepest part. Therefore, even when the excavation part is provided deeper than the groundwater level, the mixed purification agent does not settle down in the water in the excavation part, and the separation phenomenon of the mixed purification agent due to this sedimentation fall is prevented. The Thereby, it becomes possible to purify contaminated soil and / or groundwater efficiently.
以下、本発明についてさらに詳細に説明する。 Hereinafter, the present invention will be described in more detail.
本発明では、汚染土壌に掘削部を設け、この掘削部の最深部に浄化剤と透水用粒状物とを含む混合浄化剤を配置する。 In the present invention, an excavation part is provided in the contaminated soil, and a mixed purification agent containing the purification agent and the water-permeable granular material is disposed at the deepest part of the excavation part.
土壌を汚染している汚染物質としては、有機塩素化合物、アルカリ、フッ素、重金属などが例示される。 Examples of pollutants that contaminate the soil include organochlorine compounds, alkalis, fluorine, and heavy metals.
浄化剤としては、例えば有機塩素化合物が対象であれば浄化用金属粉、アルカリが対象であれば酸性白土、フッ素が対象であれば酸化マグネシウム、重金属が対象の場合はキレートや鉄塩、アルミニウム塩などが例示されるが、これらに限定されず浄化対象によって様々な浄化剤を採用することができる。浄化用金属粉としては例えば鉄が例示され、酸化鉄、還元鉄、合金などが好適であるが、還元鉄がより好適である。土壌が複数種類の汚染物質を含むときには、これら浄化剤を複数混合して用いることもできるし、1種又は複数種の混合浄化剤を掘削部最深部に配置した後、その上に別種の混合浄化剤を配置してもよい。 Examples of the purifying agent include metal powder for purification if an organic chlorine compound is used, acid clay if alkali is used, magnesium oxide if fluorine is used, chelate, iron salt, aluminum salt if heavy metal is used. However, the present invention is not limited to these, and various purification agents can be employed depending on the purification target. For example, iron is exemplified as the metal powder for purification, and iron oxide, reduced iron, alloy, and the like are preferable, but reduced iron is more preferable. When the soil contains a plurality of types of pollutants, a plurality of these cleaning agents can be mixed and used, or after one or a plurality of types of mixed cleaning agents are arranged at the deepest part of the excavation part, another type of mixing agent is mixed thereon. A purifier may be placed.
浄化剤の形状は特に限定されないが、例えば粒径0.1〜2mmの粗大粒子であって地下水の流動を妨げない形状のものが望ましい。 The shape of the purifier is not particularly limited, but for example, a coarse particle having a particle diameter of 0.1 to 2 mm that does not hinder the flow of groundwater is desirable.
透水用粒状物としては環境上問題ない材料であれば特に問題なく、充填状態時の透水係数が10−2〜10−3cm/sオーダーの材料、例えば砂や砂利などを好適に用いることができる。浄化剤と透水用粒状物との混合比は、体積比で1:9〜1:0.1程度が好適であるが、これに限定されない。 There are no particular problems with the water-permeable granular material as long as it is a material that is not environmentally problematic, and a material having a water permeability coefficient in the filled state of the order of 10 −2 to 10 −3 cm / s, such as sand or gravel, is preferably used. it can. The mixing ratio of the purifying agent and the water-permeable granular material is preferably about 1: 9 to 1: 0.1 in volume ratio, but is not limited thereto.
掘削部の形状は土壌を掘削した孔状でもよいし、並列に掘削孔を作るなどした溝状でもよい。孔はボーリングによって形成されるのが好ましいが、ドリリングバケット等によって形成されてもよい。孔の直径は200〜3000mm程度が好適であるが、これに限定されない。本発明は、掘削部を地下水位よりも深く形成し、掘削部下部に地下水が貯留する場合に適用するのに好適である。 The shape of the excavation part may be a hole shape obtained by excavating soil or a groove shape in which excavation holes are formed in parallel. The hole is preferably formed by boring, but may be formed by a drilling bucket or the like. The diameter of the hole is preferably about 200 to 3000 mm, but is not limited thereto. The present invention is suitable for application when the excavation part is formed deeper than the groundwater level and the groundwater is stored in the lower part of the excavation part.
容器としては、混合浄化剤を漏らすことなく収容保持でき、掘削部最深部に到達するまで、収容した混合浄化剤に混合ムラが生じず、最深部に達すると底部が開口して混合浄化剤を放出できる構造であればどのような構造のものでもよい。 As a container, the mixed purifying agent can be stored and held without leaking, and mixing unevenness does not occur in the stored mixed purifying agent until reaching the deepest part of the excavation part, and when the deepest part is reached, the bottom opens and the mixed purifying agent is removed. Any structure can be used as long as it can be released.
以下、第1図及び第2図を参照して、掘削部の最深部に混合浄化剤を配置する方法の一例について説明する。 Hereinafter, with reference to FIG. 1 and FIG. 2, an example of the method of arrange | positioning mixed purification agent in the deepest part of an excavation part is demonstrated.
第1図(a),(b)は実施の形態に係る方法によって掘削部内に混合浄化剤を配置する作業を示す断面図である。 FIGS. 1 (a) and 1 (b) are cross-sectional views showing the operation of placing the mixed purification agent in the excavation part by the method according to the embodiment.
第1図(a)の通り、地盤1に掘削部として孔2が形成されている。この孔2は地下水位よりも深く掘られている。また、この実施の形態では孔2は、オールケーシング工法によって掘削されたものである。
As shown in FIG. 1 (a), a
第1図(a)では、クレーン車3のクレーンから垂下するワイヤロープの下端に容器としてバケット4が吊り下げられている。このバケット4は、上方が開放した有底円筒形であり、第2図に示すように、底部に開閉可能な底蓋4aを備えた底開き式バケットである。このバケット4は、この底蓋4aを閉鎖状態にロックするためのロック機構(図示略)と、このロック機構のロックを解除するためのアンロックレバー4bとを有している。このアンロックレバー4bは、ロック状態ではバケット4の底面から下方に突出しており、バケット4が孔底2aに着底すると上方に押し上げられてロック機構をアンロック状態とするよう構成されている。
In FIG. 1 (a), a
第1図(a)の通り、このバケット4にパワーショベル5によって鉄粉混合砂などの混合浄化剤6を供給する。次いで、クレーン車3はこのバケット4を孔2内に入れるように自走及びブーム旋回操作され、しかる後、第1図(b)の通り、ワイヤロープを送り出し、バケット4を孔2の最深部にまで降下させる。
As shown in FIG. 1 (a), a mixed
バケット4が孔底2aに着底すると、第2図(b)の通りアンロックレバー4bが孔底2aに当って押し上げられ、ロック機構がロック解除状態となる。そこで、第2図(c)の通りバケット4を徐々に引き上げると、底蓋4aが開き出し、バケット4内の混合浄化剤6がバケット4から孔2の底部に放出される。さらにバケット4を引き上げることにより、バケット4内のすべての混合浄化剤6が放出される。
When the
このように、孔底2aに着底したバケット4から混合浄化剤6が孔底2aに徐々に放出されるので、混合浄化剤6が孔2内に溜まった地下水中を沈降落下することがない。このため、混合浄化剤の鉄粉と砂とが分離することがない。この結果、効率よく汚染土壌及び地下水の浄化処理が行われる。
As described above, the mixed
なお、容器底部から水底に鉄粉混合砂を放出しても鉄粉と砂とが分離しないことを確認するための実験例と、鉄粉混合砂を水面から投入すると分離が生じること示す対比実験例とを次に示す。 In addition, an experimental example to confirm that iron powder and sand do not separate even when iron powder mixed sand is discharged from the bottom of the container to the water bottom, and a comparison experiment showing that separation occurs when iron powder mixed sand is introduced from the water surface An example is shown below.
[実験例]
(1)第3図(a)の通り、水深1mのプール10中に水槽(高さ300mm、幅300mm、長さ300mm)11を沈設した。
(2)第3図(b)の通り、底面が開閉可能となっている容器(高さ100mm、幅100mm、長さ100mm)12内に、鉄粉と砂とを同体積で混合してなる鉄粉混合砂よりなる混合浄化剤6を充填した。なお、鉄粉の平均粒径は0.5mm、砂の平均粒径は1.0mmである。
(3)第3図(c)の通り、この容器12を水槽11の底面に着底させた。
(4)次いで、第3図(d)の通り、容器12の底部を開放すると共に容器12を引き上げ、容器12から水槽11内に混合浄化剤6を流出させた。
(5)(2)〜(4)の手順を繰り返し、水槽11内に鉄粉混合砂よりなる混合浄化剤6を充填した。
(6)プール10から水槽11を取り出し、この水槽11内の10箇所から鉄粉混合砂を採取し、鉄粉と砂を磁選して体積を測定した結果、表1のように各試料とも上面と底面とで鉄粉と砂の体積比がほぼ等しく、混合ムラなく充填できていることが判明した。
[Experimental example]
(1) As shown in FIG. 3 (a), a water tank (height 300 mm, width 300 mm, length 300 mm) 11 was set in a
(2) As shown in FIG. 3 (b), iron powder and sand are mixed in the same volume in a container (height 100 mm, width 100 mm, length 100 mm) 12 whose bottom surface can be opened and closed. A mixed
(3) As shown in FIG. 3 (c), the
(4) Next, as shown in FIG. 3 (d), the bottom of the
(5) The procedures (2) to (4) were repeated, and the
(6) The
なお、表1の第1〜第4の隅部は、水槽11内の4個の隅部を意味する。
In addition, the 1st-4th corner of Table 1 means the four corners in the
[比較実験例]
第3図(a)の状態において水槽11が満杯になるまで、上記の鉄粉混合砂を水面から静かに投入した。
[Comparative experiment example]
In the state of Fig. 3 (a), the iron powder mixed sand was gently poured from the water surface until the
プール10から水槽11取り出し、この水槽内の10箇所から鉄粉混合砂を採取し、鉄粉と砂を磁選して体積を測定した結果、表1のように各試料とも上面と底面とで鉄粉と砂の体積比が異なっており、充填に際して分離してしまい混合ムラが生じていることが判明した。
The
1 地盤
2 孔
3 クレーン車
4 容器
5 パワーショベル
6 混合浄化剤
DESCRIPTION OF
Claims (3)
底部が開閉可能な容器内に該混合浄化剤を収容し、該容器を掘削部の最深部に下ろし、次いで該容器の底部を開放して混合浄化剤を放出させることにより、該掘削部内に該混合浄化剤を配置することを特徴とする汚染土壌中に浄化剤を配置する方法。 It is a method of arranging a mixed purification agent containing a purification agent and water-permeable granular material in the deepest part of the soil excavation part,
The mixed purification agent is contained in a container whose bottom can be opened and closed, the container is lowered to the deepest part of the excavation part, and then the bottom of the container is opened to release the mixed purification agent, whereby the mixed purification agent is released into the excavation part. A method for disposing a purification agent in contaminated soil, characterized by disposing a mixed purification agent.
底部が開閉可能な容器内に該混合浄化剤を収容し、該容器を掘削部の最深部に下ろし、次いで該容器の底部を開放して混合浄化剤を放出させることにより、該掘削部内に該混合浄化剤を配置することを特徴とする汚染土壌及び/又は地下水の原位置浄化方法。 A contaminated soil having an excavation part in the contaminated soil, a mixed purification agent including a purification agent and a water-permeable granular material disposed in the deepest part of the excavation part, and purifying the soil and / or groundwater with the mixed purification agent and / or Or an in-situ purification method of groundwater,
The mixed purification agent is accommodated in a container whose bottom can be opened and closed, the container is lowered to the deepest part of the excavation part, and then the bottom part of the container is opened to release the mixed purification agent, whereby the mixed purification agent is released into the excavation part. An in-situ purification method for contaminated soil and / or groundwater, wherein a mixed purification agent is disposed.
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JP2016087558A (en) * | 2014-11-06 | 2016-05-23 | 大成建設株式会社 | Formation method of soil purification wall and putting can |
CN112452190A (en) * | 2020-11-20 | 2021-03-09 | 河南城建学院 | Mixing mechanism and ecological soil remediation device for administering |
CN116967265A (en) * | 2023-09-22 | 2023-10-31 | 山西省生态环境监测和应急保障中心(山西省生态环境科学研究院) | Soil pollution treatment device |
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