JP2007090301A - Method for purifying heavy metal contaminated soil - Google Patents
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本発明は、地上構造物の地下になどに存在する重金属類を含んだ土壌の浄化処理方法に関し、更に詳しくは、重金属類を含んだ土壌から重金属類を効率的に除去する方法に関する。 The present invention relates to a method for purifying soil containing heavy metals existing in the underground of a ground structure, and more particularly to a method for efficiently removing heavy metals from soil containing heavy metals.
昨今、市街地再開発による調査の増加に伴い、工場跡地等の重金属汚染が判明する事例が増加している。平成14年の土壌汚染対策法の成立により、かかる土壌汚染に対する法制度が整備され、汚染除去処置等の事例が今後大幅に増加することが予測される。
一方、工場跡地等に建設した地上構造物(ビル、公共施設、一般家屋等)は、当該構造物の地下に土壌汚染の存在があることを知らずに、また十分な汚染調査を行わずに当該構造物を建設したことが多く、当該構造物建設後、土壌汚染が発覚し、近年、大きな社会問題となっている。
In recent years, with the increase in surveys due to urban redevelopment, there have been an increase in cases where heavy metal contamination is found in factory sites and the like. With the establishment of the Soil Contamination Countermeasures Law in 2002, a legal system for such soil contamination is established, and it is predicted that cases such as decontamination procedures will increase significantly in the future.
On the other hand, ground structures (buildings, public facilities, general houses, etc.) constructed on the site of the factory are not subject to the presence of soil contamination in the basement of the structure, and are not subject to sufficient contamination investigations. In many cases, a structure has been constructed, and after the construction of the structure, soil contamination has been detected, which has become a major social problem in recent years.
土壌の重金属汚染に対して、現在の国内で行われている汚染対策は、不溶化処理、覆土工事、遮水工事など、周辺環境から汚染源から遮断する方法が一般的であるが、これらの方法は重金属類を現場に残したままであることから、環境の変化により再溶出して汚染を引き起こす危険性が残るうえ、希少資源の節約の観点からも好ましい方法とは言えず、かかる土地の資産価値が損なわれる可能性が存在する。 The current domestic pollution control measures against heavy metal contamination of soil include methods such as insolubilization, soil covering work, water shielding work, etc., which are isolated from the source of contamination from the surrounding environment. Since heavy metals are left on site, there remains a risk of re-elution due to environmental changes and causing pollution, and it is not a preferable method from the viewpoint of saving scarce resources. There is potential for damage.
近年、汚染土壌を掘削し、清浄な土壌と入れ替え、汚染土壌を産業廃棄物として処分する方法が多くが、最終処分場の逼迫が社会問題となっており、好ましい方法とは言いがたく、また、すでに当該土地に地上に構造物が建設されている場合には、構造物を一旦解体した後、汚染土壌を搬出する必要があり、膨大な費用を要するため、決して好ましい方法とは言えない。また、既に地上構造物が建設されている場合には重金属を効率良く、また、完全に不溶化することができない。このような背景の下、地上構造物を解体することなく、原位置で汚染された土壌を浄化する方法が、強く望まれている。にもかかわらず原位置で汚染した土壌を浄化する方法に関しては、環境に負荷のかかる有機溶媒を用いたり、水位勾配を用いる為抽出が不完全であったり、いずれもまだ十分に上記の問題を解決できる技術に至っていない(例えば特許文献1〜3参照。)。 In recent years, there are many methods of excavating contaminated soil, replacing it with clean soil, and disposing of contaminated soil as industrial waste. When a structure has already been built on the land, it is necessary to dismantle the structure and then carry out the contaminated soil, which requires enormous costs and is not a preferable method. In addition, when a ground structure has already been constructed, heavy metals cannot be efficiently and completely insolubilized. Under such a background, a method for purifying soil contaminated in situ without dismantling the ground structure is strongly desired. Nevertheless, regarding the method of remediating soil contaminated in-situ, organic solvents that are burdensome to the environment are used, or extraction is incomplete due to the use of a water level gradient. It has not reached the technique which can be solved (for example, refer patent documents 1-3).
本発明は、上記のような従来技術の課題を背景になされたもので、その目的は、原位置において土壌中の有害金属を土壌中から分離・除去するとともに、汚染土壌を浄化土壌として修復する方法を提供することにある。 The present invention has been made against the background of the problems of the prior art as described above, and its purpose is to separate and remove harmful metals in the soil from the soil and restore the contaminated soil as purified soil. It is to provide a method.
本発明者らは、上記した従来技術に鑑み、鋭意検討を重ねた結果、地上構造物の地下に存在する重金属含有汚染土壌を浄化する方法であって、該汚染土壌を下記(a)〜(e)の工程を実施することにより原位置のままで重金属を洗浄剤水溶液で洗浄除去することを特徴とする汚染土壌の浄化方法により、汚染土壌中から有害金属を分離・除去するとともに副生廃棄物を出さず、汚染土壌を浄化土壌として修復する方法を完成するに至った。
(a)重金属含有汚染土壌を包囲する止水壁を土中に設置する工程
(b)止水壁内の重金属含有汚染土壌に洗浄剤水溶液供給用井戸及び揚水用井戸を設置する工程
(c)洗浄剤水溶液供給用井戸内に洗浄剤水溶液を注入して、止水壁内の重金属含有汚染土壌全体を洗浄剤水溶液に浸漬させる工程
(d)揚水用井戸から洗浄剤水溶液を揚水すると同時に洗浄剤水溶液を追加注入する工程
(e)揚水用井戸から洗浄剤水溶液を揚水すると同時に水を注入し、洗浄剤水溶液を除去する工程
As a result of intensive studies in view of the above-described conventional technology, the present inventors are a method for purifying heavy metal-containing contaminated soil existing underground in a ground structure, and the contaminated soil is represented by the following (a) to ( e) Remove and remove hazardous metals from contaminated soil and remove by-products using a contaminated soil remediation method, characterized in that heavy metals are washed and removed with an aqueous cleaning agent solution in situ. It came to complete the method of repairing the contaminated soil as a purified soil without putting out anything.
(A) A step of installing a water blocking wall surrounding the heavy metal-containing contaminated soil in the soil (b) A step of installing a cleaning solution supply well and a pumping well on the heavy metal-containing contaminated soil in the water blocking wall (c) Injecting the cleaning solution into the cleaning solution supply well and immersing the entire heavy metal-containing contaminated soil in the water blocking wall in the cleaning solution (d) Pumping the cleaning solution from the pumping well and simultaneously cleaning the cleaning solution Step of additionally injecting aqueous solution (e) Step of removing the aqueous cleaning solution by simultaneously injecting water from the well for pumping and injecting water
以上に説明した本発明によれば、地上構造物を解体することなく、土壌中の有害金属を効率よく、汚染土壌を浄化土壌に修復する方法として極めて有用である。 According to the present invention described above, it is extremely useful as a method for efficiently removing harmful metals in soil and repairing contaminated soil to purified soil without dismantling the above ground structure.
以下、本発明の実施の形態について詳細に説明する。本発明が浄化の対象とする汚染土壌に含有される重金属としては、例えば、カドミウム、銅、鉛、砒素、クロム、セレン、水銀、カルシウム、鉄、アルミニウムを挙げることができる。これらの重金属類の土壌中における存在形態は特に限定されないが、通常、イオン、酸化物、水酸化物などの状態で含有されている場合が多い。 Hereinafter, embodiments of the present invention will be described in detail. Examples of heavy metals contained in the contaminated soil to be purified by the present invention include cadmium, copper, lead, arsenic, chromium, selenium, mercury, calcium, iron, and aluminum. Although the presence form in the soil of these heavy metals is not specifically limited, Usually, it contains in the state of an ion, an oxide, a hydroxide, etc. in many cases.
(a)重金属含有汚染土壌を包囲する止水壁を土中に設置する工程について
本発明においては、先ず、ビル、マンション、会館、講堂、集会所などの地上構造物の地下に存在する汚染土壌を包囲する止水壁を土中に設置する。止水壁は、不透水性地盤に到る長さで、汚染土壌を封じ込めるよう設置するのが好ましい。その際の止水壁は洗浄剤水溶液を透水させないものであればよく、例えば、鋼矢板、ソイルセメント連続壁等を挙げることができる。また洗浄剤水溶液が透水しない、強度が十分である、設置工程が非常に困難なものにならない等の十分な厚さを持っていることが好ましい。止水壁をこのように設置しないと、後の工程で注入する洗浄剤水溶液が浄化すべき土壌よりも拡散しやすい土壌へ多量に流れ込むことがあり好ましくない。例えば鋼矢板を用いる場合には土壌中に鋼矢板をほぼ垂直に設置する手法にて設置することができる。ソイルセメントを用いる場合には流動化させたソイルセメント壁に垂直にシートを挿入していく方法、流動化したソイルセメント壁にロール状シートを挿入し横方向に引く遮水止水壁工法(ラテナビウォール工法)を用いることができる。他通常土木分野で用いられているような手法によっても良い。
(A) About the process of installing a water blocking wall surrounding the heavy metal-containing contaminated soil in the soil In the present invention, first, the contaminated soil present in the ground of a ground structure such as a building, condominium, hall, auditorium, meeting place, etc. Install a water barrier in the soil that surrounds It is preferable to install the water blocking wall so as to contain the contaminated soil with a length reaching the impermeable ground. The water stop wall in that case should just be a thing which does not permeate | transmit a cleaning agent aqueous solution, For example, a steel sheet pile, a soil cement continuous wall, etc. can be mentioned. Further, it is preferable that the cleaning agent aqueous solution has a sufficient thickness such that water does not pass through, the strength is sufficient, and the installation process does not become very difficult. If the water blocking wall is not installed in this way, it is not preferable because a large amount of the aqueous cleaning solution injected in the subsequent process flows into the soil that is more likely to diffuse than the soil to be purified. For example, when a steel sheet pile is used, the steel sheet pile can be installed in the soil almost vertically. When soil cement is used, a sheet is inserted vertically into the fluidized soil cement wall, a roll-off sheet wall is inserted into the fluidized soil cement wall and pulled horizontally. Navi Wall Construction Method) can be used. Other methods that are usually used in the civil engineering field may also be used.
(b)止水壁内の重金属含有汚染土壌に洗浄剤水溶液供給用井戸及び揚水用井戸を設置する工程について
次に、封じ込めた汚染土壌内にボーリング等により、洗浄剤水溶液を供給する為の洗浄剤水溶液供給用井戸、洗浄剤水溶液をくみ上げるための揚水用井戸を設置する。より具体的な井戸の掘削方法としては、圧入工法、無排土孔壁工法、中堀杭工法、鋼管ソイルセメント杭工法等通常用いられている手法により設置することができる。引き続いて、当該洗浄剤水溶液供給用井戸より汚染土壌内に洗浄剤水溶液を供給し、該汚染土壌より重金属成分を抽出する。各々の井戸の数については限定されたものではなく、汚染された土壌の量に応じて選ぶことが好ましい。また各々の洗浄剤水溶液供給用井戸、揚水用井戸間の距離は特に限定されるものではないが、包囲された土壌の領域から考慮されうる程度の適切な距離をつけて設置することが好ましい。
(B) About the process of installing a cleaning solution supply well and a pumping well in heavy metal-containing contaminated soil in the water blocking wall Next, cleaning to supply the cleaning solution by boring into the contaminated contaminated soil A well for supplying an aqueous solution and a well for pumping up a cleaning solution will be installed. As a more specific method of excavating a well, it can be installed by a commonly used technique such as a press-in method, a no-drainage wall method, a Nakabori pile method, a steel pipe soil cement pile method. Subsequently, a cleaning solution is supplied into the contaminated soil from the cleaning solution supply well, and heavy metal components are extracted from the contaminated soil. The number of each well is not limited and is preferably selected according to the amount of contaminated soil. The distance between each of the cleaning solution supply well and the pumping well is not particularly limited, but it is preferable that the wells are installed with an appropriate distance that can be taken into consideration from the surrounded soil region.
(c)洗浄剤水溶液供給用井戸内に洗浄剤水溶液を注入して、止水壁内の重金属含有汚染土壌全体を洗浄剤水溶液に浸漬させる工程について
用いる洗浄剤としては、上述の重金属成分を抽出できるものであれば特に限定されず、例えば、塩酸、硝酸などの無機酸、酢酸やクエン酸、酒石酸、更にエチレンジアミン四酢酸(EDTA)を代表とする有機酸成分や苛性ソーダなどのアルカリ等、任意の洗浄剤を用いることができる。しかし、ほとんどの地上構築物は地下にセメントを使用した構造物が存在しており、セメント保護する観点から洗浄剤の水溶液のpHを4以上に調整することが好ましい。pHの調整に使用する調整剤は特に限定されるものではなく、苛性ソーダ、酢酸、塩酸などを使用することができる。さらにpHを一定値に調節するために例えば「化学便覧基礎編」改訂3版のII巻354頁(社団法人日本化学会編、丸善(株)発行、1984年6月25日発行)に記載されているような緩衝液を用いることもできる。
(C) About the process of injecting the detergent aqueous solution into the well for supplying the detergent aqueous solution and immersing the entire heavy metal-containing contaminated soil in the water blocking wall in the detergent aqueous solution As the detergent to be used, the above heavy metal components are extracted. It is not particularly limited as long as it can be used. For example, inorganic acids such as hydrochloric acid and nitric acid, acetic acid, citric acid, tartaric acid, organic acid components represented by ethylenediaminetetraacetic acid (EDTA), alkalis such as caustic soda, etc. A cleaning agent can be used. However, most ground structures have structures using cement underground, and it is preferable to adjust the pH of the aqueous solution of the cleaning agent to 4 or more from the viewpoint of protecting the cement. The adjusting agent used for adjusting the pH is not particularly limited, and caustic soda, acetic acid, hydrochloric acid and the like can be used. In order to further adjust the pH to a certain value, it is described in, for example, “Chemical Handbook Basic Edition”, revised edition, Volume II, page 354 (edited by the Chemical Society of Japan, published by Maruzen Co., Ltd., published on June 25, 1984). It is also possible to use such a buffer solution.
汚染された土壌中の重金属は一般的に土壌の深層部には少なく、土壌の上層部に存在する可能性が高いことは公知である。しかし、洗浄時には汚染土壌を効率よく洗浄するため、汚染土壌表面位置まで洗浄剤水溶液を満たし、洗浄剤水溶液に汚染土壌が浸漬した状態とする。また、洗浄剤水溶液の供給方法についても特に限定されるものではない。汚染土壌から効率よく重金属を抽出するため、洗浄剤水溶液に土壌が浸漬した状態を一定時間以上保持することが好ましく、保持時間は土壌により異なるが通常数時間〜7日程度保持することが好ましい。具体的には1時間〜7日間、より好ましくは2時間〜7日間が好ましい。以上の(a)〜(c)工程は逐次的に実施されることが好ましい。 It is known that heavy metals in contaminated soil are generally low in the deep part of the soil and are likely to exist in the upper part of the soil. However, in order to wash the contaminated soil efficiently at the time of washing, the detergent aqueous solution is filled to the surface position of the contaminated soil, and the contaminated soil is immersed in the detergent aqueous solution. Further, the method of supplying the cleaning agent aqueous solution is not particularly limited. In order to efficiently extract heavy metals from the contaminated soil, it is preferable to maintain a state in which the soil is immersed in the cleaning agent aqueous solution for a predetermined time or more, and the retention time varies depending on the soil, but is usually preferably maintained for several hours to 7 days. Specifically, it is preferably 1 hour to 7 days, more preferably 2 hours to 7 days. The above steps (a) to (c) are preferably performed sequentially.
(d)揚水用井戸から洗浄剤水溶液を揚水すると同時に洗浄剤水溶液を追加注入する工程及び(e)揚水用井戸から洗浄剤水溶液を揚水すると同時に水を注入し、洗浄剤水溶液を除去する工程について
重金属成分を抽出した洗浄剤水溶液は、揚水用井戸から、ポンプにより揚水され、土中より回収される。この際、土壌中の局所的水分変化による地盤沈下などの問題を防止するため、揚水すると同時に、揚水量と同じ量だけ別の井戸から注水することが好ましい。浸漬することにより洗浄剤水溶液の注入速度および揚水速度は重金属洗浄効率には差は生じないが、土壌性質により透水係数が異なり、注入および揚水の速度が上がるにつれて微細土壌が洗浄剤水溶液と共に揚水されるため、土壌性質を調査して決定することが好ましい。土壌中の重金属成分をさらに回収するため、例えば上述の注水の代わりに新たな洗浄剤水溶液の注入・再洗浄を繰り返し実施しても良い。またこの作業の順序は特に限定されることはなく、揚水すると同時に揚水量と同量の注水を行ってもよく、また揚水すると同時に揚水量と同量の洗浄剤水溶液を追加注入しても良い。好ましくは洗浄剤追加注入を十分な回数及び十分な量注入してから水を注水するのが好ましい。
(D) A step of pumping a cleaning agent aqueous solution from a well for pumping and simultaneously injecting a cleaning agent aqueous solution at the same time. (E) A step of pumping a cleaning agent aqueous solution from a pumping well and simultaneously injecting water to remove the cleaning solution. The cleaning agent aqueous solution from which the heavy metal component has been extracted is pumped from the pumping well by a pump and collected from the soil. At this time, in order to prevent problems such as land subsidence due to local moisture changes in the soil, it is preferable to pump water from another well at the same time as the amount of pumped water. The soaking rate and pumping rate of the cleaning agent aqueous solution do not differ in the heavy metal cleaning efficiency by soaking, but the hydraulic conductivity varies depending on the soil properties. Therefore, it is preferable to investigate and determine the soil properties. In order to further collect heavy metal components in the soil, for example, instead of the above-described water injection, injection and re-washing of a new detergent aqueous solution may be repeated. The order of this operation is not particularly limited, and the same amount of water as that of the pumped water may be injected at the same time as the water is pumped. . Preferably, it is preferable to inject the water after injecting the cleaning agent additional injection a sufficient number of times and in a sufficient amount.
揚水した洗浄剤水溶液中の重金属濃度の推移などより、施工前に設定した浄化水準を達成した後には洗浄剤水溶液を水に変えて注水および揚水を繰り返し実施することにより残存する洗浄剤を除去する。
このようにして重金属の含有量が低減された土壌は、浄化土壌として得られる。一方揚水された重金属を含む洗浄剤水溶液などの排水は、活性炭吸着処理やキレート吸着処理、アルカリ沈殿処理、などの重金属処理装置により、重金属成分を除去した後、必要に応じて有機物除去処理を行った後、公共水域へと放流される。
After achieving the purification level set before construction due to changes in the concentration of heavy metals in the pumped detergent aqueous solution, the remaining detergent is removed by repeatedly injecting and pumping water after changing the detergent aqueous solution to water. .
Thus, the soil in which the content of heavy metals is reduced is obtained as purified soil. On the other hand, wastewater such as detergent aqueous solution containing pumped heavy metal is removed by heavy metal processing equipment such as activated carbon adsorption treatment, chelate adsorption treatment, alkaline precipitation treatment, etc., and then organic matter removal treatment is performed as necessary. And then released into public waters.
以下、本発明の一態様を模式的に表した図1を用いて具体的に説明するが、本発明はこれにより何ら限定を受けるものではない。本発明においては、先ず地上構造物(図中10)の地下に存在する重金属を含む汚染土壌(図中1)の周囲を不透水地盤(図中9)に至る止水壁(図中2)で囲いこみ、封じ込める。封じ込めた重金属類を含有する土壌(図中1)の中に注水井戸(図中3)を設置し、注水井戸より洗浄剤水溶液(図中5)を注水ポンプ(図中6)を用いて注入する。揚水井戸(図中4)より揚水ポンプ(図中7)にて、揚水する。揚水した重金属含有洗浄剤水溶液は、排水処理装置(図中8)により重金属を除去した後、放流される。 Hereinafter, although it demonstrates concretely using FIG. 1 which represented typically the one aspect | mode of this invention, this invention does not receive any limitation by this. In the present invention, a water blocking wall (2 in the figure) that first reaches the impervious ground (9 in the figure) around the contaminated soil (1 in the figure) containing heavy metals existing underground in the ground structure (10 in the figure). Enclose and contain. A water injection well (3 in the figure) was installed in the soil containing heavy metals contained (1 in the figure), and an aqueous cleaning solution (5 in the figure) was injected from the water injection well using a water injection pump (6 in the figure). To do. Water is pumped from a pumping well (4 in the figure) by a pump (7 in the figure). The heavy metal-containing cleaning solution that has been pumped is discharged after the heavy metal is removed by the waste water treatment device (8 in the figure).
以上で本発明の実施形態を説明したが、本発明は上記実施形態に限定されず、本発明の要旨を逸脱しない範囲で工程の細部や使用する装置類については適宜設計変更が可能であることは当然である。 Although the embodiment of the present invention has been described above, the present invention is not limited to the above-described embodiment, and the design details can be appropriately changed for the details of the process and the devices to be used without departing from the gist of the present invention. Is natural.
本発明の方法は地上構造物が建造されていたとしても、その地上構造物を解体することなく、また汚染された土壌を他の場所に運搬することもなく、土壌中の有害金属を効率よく、汚染土壌を浄化土壌に修復する方法として極めて有用である。重金属による汚染が懸念される化学廃棄物の埋立地等の汚染場所の土壌の浄化に効率的に適用することができる。 The method of the present invention efficiently removes harmful metals in the soil without dismantling the ground structure and transporting the contaminated soil to another place even if the ground structure is built. It is extremely useful as a method for restoring contaminated soil to purified soil. It can be efficiently applied to the purification of soil in contaminated places such as landfills for chemical wastes where contamination by heavy metals is a concern.
1 重金属類を含有する汚染土壌
2 止水壁
3 注水井戸(洗浄剤水溶液供給用井戸)
4 揚水用井戸
5 洗浄剤水溶液
6 注水ポンプ
7 揚水ポンプ
8 排水処理装置
9 不透水性地盤
10 地上構造物
1 Contaminated soil containing
4 Well for pumping 5
7 Pumping pump 8 Wastewater treatment device 9
Claims (3)
(a)重金属含有汚染土壌を包囲する止水壁を土中に設置する工程
(b)止水壁内の重金属含有汚染土壌に洗浄剤水溶液供給用井戸及び揚水用井戸を設置する工程
(c)洗浄剤水溶液供給用井戸内に洗浄剤水溶液を注入して、止水壁内の重金属含有汚染土壌全体を洗浄剤水溶液に浸漬させる工程
(d)揚水用井戸から洗浄剤水溶液を揚水すると同時に洗浄剤水溶液を追加注入する工程
(e)揚水用井戸から洗浄剤水溶液を揚水すると同時に水を注入し、洗浄剤水溶液を除去する工程 A method for purifying heavy metal-containing contaminated soil existing underground, wherein the contaminated soil is subjected to the following steps (a) to (e) so that heavy metals can be washed with an aqueous solution of a cleaning agent in situ. A method for purifying contaminated soil, comprising washing and removing.
(A) A step of installing a water blocking wall surrounding the heavy metal-containing contaminated soil in the soil (b) A step of installing a cleaning solution supply well and a pumping well on the heavy metal-containing contaminated soil in the water blocking wall (c) Injecting the cleaning solution into the cleaning solution supply well and immersing the entire heavy metal-containing contaminated soil in the water blocking wall in the cleaning solution (d) Pumping the cleaning solution from the pumping well and simultaneously cleaning the cleaning solution Step of additionally injecting aqueous solution (e) Step of removing the aqueous cleaning solution by simultaneously injecting water from the well for pumping and injecting water
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|---|---|---|---|
| JP2005286507A JP2007090301A (en) | 2005-09-30 | 2005-09-30 | Method for purifying heavy metal contaminated soil |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2005286507A JP2007090301A (en) | 2005-09-30 | 2005-09-30 | Method for purifying heavy metal contaminated soil |
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| JP2007090301A true JP2007090301A (en) | 2007-04-12 |
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Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2009006265A (en) * | 2007-06-28 | 2009-01-15 | Seibu Construction Co Ltd | Soil treatment system |
| JP2009297617A (en) * | 2008-06-11 | 2009-12-24 | Takeo Suzuki | Method for improving contaminated soil |
| JP2011256670A (en) * | 2010-06-11 | 2011-12-22 | Ohbayashi Corp | Pumping device, soft ground improvement method, ground excavation method, contaminated soil purification method and recharge method |
| JP2014023992A (en) * | 2012-07-25 | 2014-02-06 | Ohbayashi Corp | Method for treating contaminated ground in situ |
| CN104841692A (en) * | 2015-05-07 | 2015-08-19 | 天津师范大学 | Application of siduron in reinforcing extraction of municipal refuse compost heavy metal by virtue of turfgrass |
| JP2015147198A (en) * | 2014-02-07 | 2015-08-20 | 株式会社熊谷組 | System for remediation of contaminated soil and underground water |
| JP2019037930A (en) * | 2017-08-24 | 2019-03-14 | 清水建設株式会社 | Method for treating selenium-containing soil or rock |
| JP2019037929A (en) * | 2017-08-24 | 2019-03-14 | 清水建設株式会社 | Treatment of selenium-containing soil and rock |
-
2005
- 2005-09-30 JP JP2005286507A patent/JP2007090301A/en active Pending
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2009006265A (en) * | 2007-06-28 | 2009-01-15 | Seibu Construction Co Ltd | Soil treatment system |
| JP2009297617A (en) * | 2008-06-11 | 2009-12-24 | Takeo Suzuki | Method for improving contaminated soil |
| JP2011256670A (en) * | 2010-06-11 | 2011-12-22 | Ohbayashi Corp | Pumping device, soft ground improvement method, ground excavation method, contaminated soil purification method and recharge method |
| JP2014023992A (en) * | 2012-07-25 | 2014-02-06 | Ohbayashi Corp | Method for treating contaminated ground in situ |
| JP2015147198A (en) * | 2014-02-07 | 2015-08-20 | 株式会社熊谷組 | System for remediation of contaminated soil and underground water |
| CN104841692A (en) * | 2015-05-07 | 2015-08-19 | 天津师范大学 | Application of siduron in reinforcing extraction of municipal refuse compost heavy metal by virtue of turfgrass |
| JP2019037930A (en) * | 2017-08-24 | 2019-03-14 | 清水建設株式会社 | Method for treating selenium-containing soil or rock |
| JP2019037929A (en) * | 2017-08-24 | 2019-03-14 | 清水建設株式会社 | Treatment of selenium-containing soil and rock |
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