JP3846870B2 - Contaminated groundwater recovery method and its equipment - Google Patents
Contaminated groundwater recovery method and its equipment Download PDFInfo
- Publication number
- JP3846870B2 JP3846870B2 JP2002176507A JP2002176507A JP3846870B2 JP 3846870 B2 JP3846870 B2 JP 3846870B2 JP 2002176507 A JP2002176507 A JP 2002176507A JP 2002176507 A JP2002176507 A JP 2002176507A JP 3846870 B2 JP3846870 B2 JP 3846870B2
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- Prior art keywords
- suction
- nozzle
- contaminated groundwater
- discharge
- discharge path
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Description
【0001】
【産業上の利用分野】
本発明は工場廃棄物の杜撰な管理、排水設備の破損等によって地中に浸透したトリファロメロン等の揮発性有機化合物で汚染され、地中に滞留する汚染地下水の浄化回復を行うための汚染地下水回収工法とその装置に関するものである。
【0002】
【発明が解決しようとする課題】
従来、化学物質に汚染された地下水が地盤内に滞留する場合、汚染箇所周辺に遮水壁を築造して内部に井戸を堀って地下水を汲み上げ、浄化後に復水することによって行われてきた。
【0003】
しかしながら、この方法によると汚染された地下水と健全な地下水が区別なく汲み上げられるため、地下水の洗浄に長期間が必要となり必要以上に多量な地下水の処理を行わなければならなかった。
【0004】
【課題を解決するための手段】
本発明は上記した課題に対応しようとするものであり、側壁に設けた吐出ノズルから所定間隔を置いた部位に吸入孔を設け、吸入孔を吸引機構を備えた排出経路に連通させた吸引ロッドを、対象地盤の汚染地下水滞留層に挿入し、吐出ノズルから清水を吐出しながら吸引ロッドを回動して清水と汚染地下水とを攪拌混合すると共に汚染地下水を希釈化して吸入孔から吸引し、ロッド内の排出経路を通じて汚染物質の分離、気化を促進する回収槽に排出回収するようにしたものである。
【0005】
また、吐出ノズルから吐出する清水の代わりに、炭酸水(H2CO3 )を噴射吐出し、炭酸水によって汚染物質を吸着分離するようにし、回収後の浄化処理を効率化するようにした。
【0006】
また、排出経路の吸引機構を、排出経路の底部に設けたジェット噴射孔から吸引水排出方向にジェット流を噴射すると共に、その外側に排出経路内を旋回する旋回流を噴射する構成とし、ジェット流にエアーを添加するようにし、吸引回収中の汚染地下水にエアーを混入させ、地下水に溶け込んだ汚染物質の気化作用を助長し、併せて吸引ロッド自体に吸引力と搬送力が備えられるようにした。
【0007】
また、排出方向へのジェット流による推進のみでなく、旋回流噴射を加えて排出経路内壁面を均沾する強力な旋回推進流を用い、これを排出経路の中間位置にも出力地点を配置出来るようにして全経路無理のない推進力を確保した。
【0008】
なお、破砕吸引除去する汚染土壌の形態によっては、排出経路の底部中央に設定されるジェット噴射孔には、気体ジェットのみでなく清水等の液体ジェットを使用することにより、高い質量による強力な推進エネルギーを発生できる。
【0009】
ジェット噴射による排出方向への直線的エネルギーは、旋回流噴射ノズルからの旋回流と合流して旋回流の核を構成する。ジェット噴射を所定長さインナーチューブによって囲障するとジェット流はインナーチューブによって集束された後、拡散するので更に効果を高めることができる。
【0010】
旋回流は吸引ポンプだけによっては確保できない吸引搬送力を増強して質量のある汚染地下水を押し出す支持力として働き、ジェット噴射がこれと合体して排出方向への推進力を増幅する。ジェット流、旋回流を構成する流体は、それぞれ液体気体等の気相や質量を選択調整することにより、状況に応じた排出効果を構成することができる。
【0011】
【実施例】
以下図面に従って本発明の実施例を説明する。1は吸引ロッドで操作機構(目的に応じて水平方向への前進、後退など形態が異なる)2によって支持され、下降、上昇、回転若しくは360度往復回動等の作動を与えられる。
【0012】
吸引ロッド1の先端部側壁には核ノズル31、囲周ノズル32によって構成される重合吐出ノズル3が設けられ、吸引ロツド内部には吐出ノズル3や吸入孔5の各開口部に開口する多重経路を有している。
【0013】
重合吐出ノズル3は、スイベル4を介して各供給経路により供給される清水、エアー、炭酸水等を、各別の経路から開口する核ノズル31或いは囲周ノズル32を通じて地中に吐出する。
【0014】
5は吸入孔で、重合吐出ノズル3の上部(必要に応じて下部でも勿論良い)に所定の間隔を置いて開口し、排出経路6に形成された吸引機構と吸引ポンプの作動によって汚染地下水を吸入し、地上の汚染土壌処理機構10に揚送する。51は核ノズル31に清水を供給する清水供給管、52は囲周ノズル32、傾斜噴射ノズル81等に圧縮空気を供給するエア供給管、53はジェット供給管である。
【0015】
吸入孔5が開口する排出経路6の底部には、中央にスライム排出方向にジェット流を噴射するジェット噴射孔7、その外側に排出経路内を旋回する旋回流を噴射する旋回流噴射ノズル8が複数の傾斜噴射ノズル81によって構成されている。
【0016】
更に、排出経路6の内壁には所定間隔毎にジェット噴射孔もしくは旋回流噴射ノズルによる中継ノズル9が必要に応じて配置される。
【0017】
ジェット噴射孔7は周囲をインナーチューブ71によって所定長さ囲障され、ジェット流が所定長さ収束されるようになっている。なお、インナーチューブ71は設置を省略しても良い。
【0018】
以上のような装置システムにより、注入ロッド1は回転等の適宣手段によって対象地盤の汚染地下水滞留層に推進挿入される。
【0019】
汚染地下水滞留層において、重合吐出ノズル3の核ノズル31から清水若しくは炭酸水を、囲周ノズル32からエアーを吐出しながら吸引ロッド1を回動させ、汚染水と清水若しくは炭酸水を攪拌混合すると共にエアー添加を行いながら吸引ポンプを作動させてポンプの吸引力と排出経路6の吸引負圧によってエアー添加した滞留汚染水を吸入孔5から吸入する。
【0020】
吸入された汚染水は、排出経路6の底部に開口するジェット噴射孔7、その外側に配置された旋回流噴射ノズル8からの噴射によって構成されるスパイラル搬送流に乗り中継ノズル9により加速されて、排出経路6を通じて汚染地下水回収槽10に送入される。
【0021】
以上のように、炭酸水によって攪拌混合され、エアー添加された汚染地下水は、炭酸水の分離作用によって揮発性有機化合物が分離され、揮発性物質がエアー添加によって気化促進されて無害化処理されながら回収槽10に送入され、回収後、更に、無害化処理施設において処理されて行くものである。
【0022】
汚染地下水の回収された対象地盤には、吐出ノズル3を通じて清水と浄化材が注入され、環境基準の回復が行われるものである。
【0023】
本発明は以上のように構成したので、従来、大掛かりな開削工事や土留め壁の構築等が必要であった汚染地下水の除去回収を吸引ロッドの挿入によって簡易、迅速に行なうことを可能とした。
【0024】
【図面の簡単な説明】
【図1】本発明の実施例を示すもので、汚染地下水滞留層への吸引ロッドの挿入と汚染地下水吸入施工の状況を示す全体説明図
【図2】注入ロッド先端の汚染地下水吸入孔及び吐出ノズル部分の拡大縦断面図
【図3】排出経路を横断面として示したジェット噴射孔及び旋回流噴射ノズルの平面図
【符号の説明】
1 吸引ロッド
2 操作機構
3 重合吐出ノズル
31 核ノズル
32 囲周ノズル
4 スイベル
5 吸入孔
51 清水供給管
52 エア供給管
53 ジェット供給管
6 排出経路
61 吸引ポンプ
7 ジェット噴射孔
71 インナーチューブ
8 旋回流噴射ノズル
81 傾斜噴射ノズル
9 中継ノズル
10 汚染地下水回収槽
A 汚染地下水滞留層[0001]
[Industrial application fields]
The present invention is contaminated with volatile organic compounds such as trifalomeron that have penetrated into the ground due to careful management of factory waste, damage to drainage facilities, etc., and pollution for purifying and recovering contaminated groundwater that remains in the ground It relates to groundwater recovery method and its equipment.
[0002]
[Problems to be solved by the invention]
Conventionally, when groundwater contaminated with chemical substances stays in the ground, it has been done by constructing a barrier wall around the contaminated area, digging a well inside, pumping up the groundwater, and condensing it after purification. .
[0003]
However, according to this method, polluted groundwater and healthy groundwater are pumped without distinction, so it was necessary to clean the groundwater for a long time, and it was necessary to treat more groundwater than necessary.
[0004]
[Means for Solving the Problems]
SUMMARY OF THE INVENTION The present invention is intended to address the above-described problem, and a suction rod in which a suction hole is provided at a portion spaced from a discharge nozzle provided on a side wall and the suction hole is communicated with a discharge path having a suction mechanism. Is inserted into the contaminated groundwater retention layer of the target ground, the suction rod is rotated while discharging fresh water from the discharge nozzle, the fresh water and contaminated groundwater are stirred and mixed, and the contaminated groundwater is diluted and sucked from the suction hole, It is designed to be discharged and collected in a collection tank that promotes separation and vaporization of pollutants through the discharge path in the rod.
[0005]
Also, instead of fresh water discharged from the discharge nozzle, carbonated water (H 2 CO 3 ) was jetted and discharged to adsorb and separate contaminants with carbonated water, so that the purification process after recovery was made more efficient.
[0006]
In addition, the suction mechanism of the discharge path is configured to inject a jet flow in a suction water discharge direction from a jet injection hole provided at the bottom of the discharge path and to inject a swirl flow that swirls in the discharge path to the outside. Air is added to the flow, air is mixed into the contaminated groundwater during suction collection, promoting the vaporization action of the contaminants dissolved in the groundwater, and the suction rod itself is equipped with suction and transport forces did.
[0007]
In addition to propulsion by jet flow in the discharge direction, a powerful swirl propulsion flow that equalizes the inner wall of the discharge path by adding swirl flow injection can be used to place the output point at an intermediate position of the discharge path. In this way, the propulsive power without overwhelming all the routes was secured.
[0008]
Depending on the form of the contaminated soil to be crushed and removed, powerful propulsion with a high mass can be achieved by using not only a gas jet but also a liquid jet such as fresh water for the jet injection hole set at the bottom center of the discharge path. Can generate energy.
[0009]
The linear energy in the discharge direction by jet injection merges with the swirl flow from the swirl flow injection nozzle to form the core of the swirl flow. If the jet injection is obstructed by the inner tube for a predetermined length, the jet flow is focused by the inner tube and then diffused, so that the effect can be further enhanced.
[0010]
The swirling flow increases the suction conveyance force that cannot be ensured only by the suction pump and acts as a supporting force to push out the contaminated groundwater with mass, and jet jets combine with this to amplify the propulsive force in the discharge direction. The fluid constituting the jet flow and the swirl flow can constitute a discharge effect corresponding to the situation by selectively adjusting the gas phase and mass of liquid gas or the like.
[0011]
【Example】
Embodiments of the present invention will be described below with reference to the drawings. Reference numeral 1 denotes a suction rod which is supported by an operation mechanism 2 (different in form such as moving forward and backward in the horizontal direction depending on the purpose) 2 and is provided with operations such as lowering, raising, rotating or reciprocating 360 degrees.
[0012]
A
[0013]
The
[0014]
Reference numeral 5 denotes a suction hole, which opens at a predetermined interval above the superposition discharge nozzle 3 (of course, the lower part may be lower if necessary). Contaminated groundwater is removed by operating a suction mechanism and a suction pump formed in the discharge path 6. Inhaled and pumped to ground contaminated
[0015]
At the bottom of the discharge path 6 where the suction hole 5 is opened, there is a jet injection hole 7 for injecting a jet flow in the slime discharge direction at the center, and a swirl flow injection nozzle 8 for injecting a swirl flow swirling in the discharge path on the outside. A plurality of
[0016]
Further, relay nozzles 9 using jet injection holes or swirling flow injection nozzles are arranged on the inner wall of the discharge path 6 at predetermined intervals as needed.
[0017]
The jet injection hole 7 is surrounded by an
[0018]
By the apparatus system as described above, the injection rod 1 is propelled and inserted into the contaminated groundwater retention layer of the target ground by appropriate means such as rotation.
[0019]
In the contaminated groundwater retention layer, the suction rod 1 is rotated while discharging fresh water or carbonated water from the
[0020]
The sucked contaminated water is accelerated by the relay nozzle 9 in a spiral conveying flow formed by jetting from the jet injection hole 7 opening at the bottom of the discharge path 6 and the swirling flow injection nozzle 8 arranged outside the jet injection hole 7. The contaminated
[0021]
As described above, in contaminated groundwater that is stirred and mixed with carbonated water and added with air, volatile organic compounds are separated by the separation action of carbonated water, while volatile substances are promoted to be vaporized by air addition and detoxified. It is sent to the
[0022]
The target ground from which the contaminated groundwater has been collected is injected with fresh water and a purification material through the
[0023]
Since the present invention is configured as described above, it has been possible to easily and quickly remove and collect contaminated groundwater, which conventionally required large-scale excavation work and construction of retaining walls, by inserting a suction rod. .
[0024]
[Brief description of the drawings]
FIG. 1 shows an embodiment of the present invention, and is an overall explanatory view showing the state of insertion of a suction rod into a contaminated groundwater retention layer and a construction procedure for sucking contaminated groundwater. FIG. Enlarged longitudinal sectional view of the nozzle part [Fig. 3] Plan view of the jet injection hole and swirl flow injection nozzle showing the discharge path as a transverse section [Explanation of symbols]
1
31 Nuclear nozzle
32 Surrounding nozzle 4 Swivel 5 Suction hole
51 Fresh water supply pipe
52 Air supply pipe
53 Jet supply pipe 6 Discharge route
61 Suction pump 7 Jet injection hole
71 Inner tube 8 Swirl nozzle
81 Inclined spray nozzle 9 Relay nozzle
10 Contaminated groundwater recovery tank A Contaminated groundwater retention layer
Claims (6)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002176507A JP3846870B2 (en) | 2002-06-18 | 2002-06-18 | Contaminated groundwater recovery method and its equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2002176507A JP3846870B2 (en) | 2002-06-18 | 2002-06-18 | Contaminated groundwater recovery method and its equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JP2004024924A JP2004024924A (en) | 2004-01-29 |
| JP3846870B2 true JP3846870B2 (en) | 2006-11-15 |
Family
ID=31174792
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2002176507A Expired - Lifetime JP3846870B2 (en) | 2002-06-18 | 2002-06-18 | Contaminated groundwater recovery method and its equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3846870B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100661277B1 (en) * | 2006-03-08 | 2006-12-28 | 강종현 | Well Regeneration Device for Vertical Sump and Regeneration Method Using the Same |
| JP7664738B2 (en) | 2021-03-31 | 2025-04-18 | 太平洋セメント株式会社 | Hexavalent chromium elution inhibitor |
-
2002
- 2002-06-18 JP JP2002176507A patent/JP3846870B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JP2004024924A (en) | 2004-01-29 |
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