JPH05323040A - Method and apparatus for monitoring flow rate and specified water quality of underground water and removing pollution thereof - Google Patents

Method and apparatus for monitoring flow rate and specified water quality of underground water and removing pollution thereof

Info

Publication number
JPH05323040A
JPH05323040A JP15014092A JP15014092A JPH05323040A JP H05323040 A JPH05323040 A JP H05323040A JP 15014092 A JP15014092 A JP 15014092A JP 15014092 A JP15014092 A JP 15014092A JP H05323040 A JPH05323040 A JP H05323040A
Authority
JP
Japan
Prior art keywords
water
pipe
concentration
sent
specified
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP15014092A
Other languages
Japanese (ja)
Other versions
JP2559654B2 (en
Inventor
Shigehiko Kimura
重彦 木村
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
NISSAKU KK
NITSUSAKU KK
Original Assignee
NISSAKU KK
NITSUSAKU KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by NISSAKU KK, NITSUSAKU KK filed Critical NISSAKU KK
Priority to JP15014092A priority Critical patent/JP2559654B2/en
Publication of JPH05323040A publication Critical patent/JPH05323040A/en
Application granted granted Critical
Publication of JP2559654B2 publication Critical patent/JP2559654B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Abstract

PURPOSE:To keep specified matters exceeding an allowable concentration from flowing down by monitoring the flow rate of underground water and specified matters to be monitored such as contaminants continuously to automatically remove the matters to be monitored. CONSTITUTION:A part of underground water to be pumped is sent to a recorder/specified matter detector 9 via a water supply pipe 10 to measure and record the concentration of individual matters. The remainder of the underground water pumped is sent to an aeration column 12 passing through a pumping pipe 11. At the column, a volatile gas is volatilized to pass through a corrector when it exceeds an allowable concentration and is discharged after it is confirmed to be below the allowable concentration. The water which passes through a filter tank 13 for filtering the specified matters via a connecting pipe 14 from the aeration column 12 is sent to the detector 9 again via a return pipe 19 from a delivery pipe 18. The concentration of each material is measured and recorded again and the water is sent to the deliver pipe 18 via a reverse return pipe 20 again. When the concentration obtained gives a value lower than all allowable concentration values of the materials, a valve 15 is changed to open and the water is sent for water injection 16 via the reverse return pipe 20 to be delivered to a location according to the purposes of application.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、地下水の流量と特定水
質を監視及び除染する方法及び装置に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for monitoring and decontaminating groundwater flow rate and specific water quality.

【0002】[0002]

【従来の技術】従来、地下水の流量の測定方法は、ダル
シー理論に基づいて直径5〜10センチメートルの円形パ
イプの一部にスクリーンを取付けた観測井を、想定する
地下水流の上流部と下流部に設け、両井の地下水位差を
距離で除した動水勾配、観測井設置時に電気検層等で得
た帯水層の厚さ、及び観測井での揚水試験で得た帯水層
の透水係数という三者の積として間接的な流量を求めて
いる。
2. Description of the Related Art Conventionally, the method of measuring the flow rate of groundwater is based on Darcy's theory. An observation well in which a screen is attached to a part of a circular pipe with a diameter of 5 to 10 cm is assumed to be located upstream and downstream of the assumed groundwater flow. Located in the area, the hydraulic gradient obtained by dividing the difference in groundwater level between the two wells by the distance, the thickness of the aquifer obtained by electrical logging when installing the observation well, and the aquifer obtained by the pumping test at the observation well. The indirect flow rate is calculated as the product of the three factors called the hydraulic conductivity of.

【0003】しかし、地下水流は帯水層内を一般に横幅
で数メートル間幅に散在するパイプ状の水みち流から成
り立つので、観測井が水みち流に出会う確率によって観
測井内の地下水位とその変動は大幅に変るという問題点
をもつ。
However, since the groundwater flow generally consists of a pipe-shaped water flow scattered in the aquifer in a width of several meters, the groundwater level in the observation well and its level depend on the probability that the observation well encounters the water flow. There is a problem that fluctuations change drastically.

【0004】従来の地下水質の測定方法は、前述した観
測井内の地下水を対象に測定するが、幅の狭い観測井が
水みち流に出会う確率の低さは、循環水中の地下水質が
観測井に出現する確率を大幅に低めている。
The conventional method of measuring groundwater quality is to measure the groundwater in the observation well described above, but the low probability of a narrow observation well encountering a water flow is due to the fact that the quality of the groundwater in the circulating water is the observation well. The probability of appearing in is greatly reduced.

【0005】従来の汚染物質のような特定水質を補集す
る方法は、前述した観測井又は同じ構造で大口径の新設
井から揚水し、揚水中の特定水質を補集する方法を用い
ている。
As a conventional method for collecting specific water quality such as pollutants, the method of collecting specific water quality in pumping water by pumping from the observation well described above or a new well having the same structure and a large diameter is used. ..

【0006】しかし、揚水による井内水位の低下で補集
範囲を広げても、循環水流の有効な補集幅は数メートル
台に止まってしまい、また揚水中には自然の帯水層内で
停滞水であった水の引き抜きや、揚水で井戸周辺から上
方に発達していく水みちを通るより浅層からの地下水の
引き込み水等が大量に混入される。これらの混入は揚水
中の特定物質の濃度を低めて回収効率を悪くし、不必要
な揚水を大量に生じ、井戸周辺では地盤沈下を引き起こ
す。さらに、揚水時以外に流れている特定物質を補集で
きない等の課題があった。
[0006] However, even if the collection range is widened by lowering the water level in the well due to pumping, the effective collection width of the circulating water flow is only in the range of several meters, and during pumping, it stagnates in the natural aquifer. A large amount of water is drawn in, and groundwater is drawn in from a shallower layer that passes through the waterway that grows upward from the well area by pumping. These contaminants lower the concentration of specific substances in the pumped water, reduce the collection efficiency, generate a large amount of unnecessary pumped water, and cause ground subsidence around the well. In addition, there was a problem that it was not possible to collect the specific substance flowing except when pumping water.

【0007】また、近年、地下水面上の不飽和層に水み
ち上の水平流が存在し、水の涵養や水質汚染に大きな役
割を果たすことが認められているが、しかし現在のとこ
ろそれを正確に回収する方法や装置は開発されていな
い。
[0007] In recent years, it has been recognized that there is a horizontal flow above the water channel in the unsaturated layer above the water table, which plays a major role in water recharge and water pollution. No method or device for accurate recovery has been developed.

【0008】[0008]

【発明が解決しようとする課題】そこで、本発明は、集
水断面を大幅に広くすることによって帯水層内の水みち
流をより確実に把握し、かつ特定物質の補集効率を高め
るようにする。
Therefore, the present invention aims to more reliably grasp the water flow in the aquifer and increase the collection efficiency of the specific substance by greatly widening the cross section of the water collection. To

【0009】また、揚水水位を常に一定に保つように揚
水し、その揚水量の経時変化を測定・記録することによ
って、地下水流量をより確実に把握するようにする。
Further, the groundwater flow rate is grasped more surely by pumping the pumped water so that the pumped water level is always kept constant and measuring and recording the change over time of the pumped water amount.

【0010】揚水水位は自然水位の最低値よりやや低い
値に設定することによって、揚水に伴う自然の停滞水の
引き込みや水みちの発達を大幅におさえ、地盤沈下を殆
ど生じないようにする。
By setting the pumping water level to a value slightly lower than the minimum value of the natural water level, the intake of natural stagnant water accompanying the pumping and the development of water channels are greatly suppressed, and the ground subsidence is hardly caused.

【0011】揚水内の特定物質の濃度を自動測定して記
録するとともに、揚水を瀑気や濾過をさせて特定物質を
取除いた後に濃度を再度測定し、許容濃度以下のときは
利用目的に応じて利用又は下水廃棄をさせるが、許容濃
度以上のときはトレンチに戻して再除染させるようにす
る。
The concentration of the specific substance in the pumped water is automatically measured and recorded, and the concentration is measured again after removing the specific substance by filtering or filtering the pumped water. Use or dispose of sewage accordingly, but when the concentration exceeds the allowable level, return it to the trench for re-decontamination.

【0012】本発明は、トレンチ工法による諸施設機能
によって、トレンチの下流部には許容濃度以上の特定物
質を流下させないようにする方法と装置を提供すること
を目的とするのである。
It is an object of the present invention to provide a method and apparatus for preventing a specific substance having a concentration higher than an allowable concentration from flowing down to the downstream portion of the trench by the various facility functions by the trench construction method.

【0013】[0013]

【課題を解決するための手段】本発明は、地下水の流量
及び汚染物等の特定の要監視物質の濃度を連続的に監視
するとともに要監視物質を自動的に除去する方法であ
る。
The present invention is a method for continuously monitoring the flow rate of groundwater and the concentration of a specific substance to be monitored such as pollutants and automatically removing the substance to be monitored.

【0014】また、この方法を実現するために、帯水層
又は及び不飽和層の上流側にスクリーンを設けたほぼ直
方体状のトレンチを設置し、このトレンチの底面部の一
部には集水溝を設け、前記底面部は集水溝方向に傾斜す
るとともに下流側に傾斜して成り、前記集水溝には吸込
口を設けるとともにこの吸込口に連設するポンプから地
上に設置した記録機兼特定物質検出機及び瀑気塔に送水
管を配設し、この瀑気塔から濾過槽に連管を配設し、こ
の濾過槽下の送出管に前記記録機兼特定物質検出機に連
結する往復管を配設し、前記送出管に設けたバルブに地
上適所に流出する注水管と再び地下のトレンチに戻す排
水管とを連設して成る装置である。
In order to realize this method, a substantially rectangular parallelepiped trench provided with a screen is installed upstream of the aquifer or the unsaturated layer, and water is collected at a part of the bottom of the trench. A recorder provided with a groove, the bottom surface of which is inclined in the direction of the water collecting groove and is inclined toward the downstream side, and the water collecting groove is provided with a suction port and is installed on the ground from a pump connected to the suction port. A water supply pipe is installed in the detector / specific substance detector and the water vapor tower, and a connecting pipe is arranged from this water vapor tower to the filter tank, and the delivery pipe under this filter tank is connected to the recorder / specific substance detector. In this device, a reciprocating pipe is installed, and a valve provided in the delivery pipe is connected to a water injection pipe that flows out to a proper place on the ground and a drain pipe that returns to the underground trench again.

【0015】[0015]

【作用】トレンチ底面部の集水溝の吸込口からポンプに
よって揚水された地下水の一部分は、給水管を経て記録
機兼特定物質検出機に送られ、ここで含有している各物
質の濃度を測定し記録するし、地下水の残部分は揚水管
から瀑気塔に送られ、ここで揮発ガスを揮発放出し、水
部分は連管を経て濾過槽に送られ、ここで特定物質を吸
着し濾過する。
[Function] Part of the groundwater pumped from the suction port of the water collection groove at the bottom of the trench is sent to the recorder and the specified substance detector via the water supply pipe, and the concentration of each substance contained here is checked. The remaining part of groundwater is sent from the pumping pipe to the waterfall tower, where volatile gas is volatilized and released, and the water part is sent to the filtration tank through the connecting pipe, where specific substances are adsorbed. Filter.

【0016】この濾過槽から一部分の水は前記記録機兼
特定物質検出機に再度送られ、物質毎の濃度を測定し記
録されるが、予定値より低い濃度となったときには、バ
ルブを開口して送水管を経て適所に送水する。
A part of the water from this filtration tank is sent to the recorder / specified substance detector again, and the concentration of each substance is measured and recorded. When the concentration becomes lower than the expected value, the valve is opened. Water to the right place via the water pipe.

【0017】もし依然として許容濃度を超えているとき
は、バルブを切換えて排水管から再びトレンチに送る。
そして、前記作用を循環して行う。
If the permissible concentration is still exceeded, the valve is switched to feed the drain pipe to the trench again.
Then, the above-mentioned action is circulated and performed.

【0018】[0018]

【実施例】 本発明のトレンチ1の構造は、対象となる
帯水層又は及び不飽和層に、例えば長さlが数メートル
から10数メートル,巾wが数10センチメートルのほぼ直
方体状に成り、その一部にはスクリーン部2を開口する
ことができる高さhを有する。
Example The structure of the trench 1 of the present invention is a substantially rectangular parallelepiped having a length l of several meters to several tens of meters and a width w of several tens of centimeters in the target aquifer or unsaturated layer. And a part thereof has a height h capable of opening the screen portion 2.

【0019】スクリーン部2を構成するトレンチ1の一
面以外の面は対象としない地層部分である。
Surfaces other than one surface of the trench 1 forming the screen portion 2 are geological layer portions not targeted.

【0020】トレンチ1は、その底面部3の一部に集水
溝4を設け、その底面部は前記集水溝4方向に傾斜する
面になるとともに地下水流の下流側に傾斜する面5を構
成し、トレンチに流入した沈降性の特定物質が集水溝4
に集まり易くする。aは上流側、bは下流側を示す。
The trench 1 is provided with a water collecting groove 4 in a part of a bottom surface portion 3, and the bottom surface portion has a surface inclined toward the water collection groove 4 and a surface 5 inclined toward the downstream side of the groundwater flow. The sedimentation specific substance that has been configured and flowed into the trench is the water collection groove 4
Make it easier to get together. “A” indicates the upstream side and “b” indicates the downstream side.

【0021】6は前記集水溝4の底部に溜まった沈降性
特定物質を吸い上げる吸込口である。
Reference numeral 6 is a suction port for sucking up the sinking specific substance accumulated at the bottom of the water collecting groove 4.

【0022】7は前記吸込口6に連接するポンプで、こ
のポンプによって所定の地下水位を保つように揚水す
る。8は所定の地下水位を保つ制御をするセンサーで、
センサーによる地下水位の経時的記録は記録機兼特定物
質検出機9において行う。
Reference numeral 7 denotes a pump connected to the suction port 6, which pumps water so as to maintain a predetermined groundwater level. 8 is a sensor that controls to keep a predetermined groundwater level,
The recording of the groundwater level by the sensor over time is performed by the recorder / specified substance detector 9.

【0023】この地下水位は、周辺の自然水位の最低値
よりもやや低い値にすることを原則とするが、地下水位
置の経年変化が大きい時や、特定物質の流入量が異常に
多い時などには、任意の水位に設定し直すことができる
機能をセンサーにもたせるようにする。
As a general rule, this groundwater level should be set to a value slightly lower than the minimum value of the surrounding natural water level, but when the secular change of the groundwater position is large, or when the inflow of a specific substance is abnormally large, etc. In addition, the sensor should have a function to reset the water level to an arbitrary level.

【0024】揚水された地下水の一部分は、給水管10を
経由して前記記録機兼特定物質検出機9に送られ、各物
質毎の濃度を測定,記録する。揚水された地下水の残部
分は、そのまま揚水管11を通って瀑気塔12に送られ、瀑
気塔で揮発性ガスを揮発させ、それが許容濃度以上のと
きは補修装置を通過させ、許容濃度以下となったことを
確認した後に放出する。
A portion of the pumped-up groundwater is sent to the recorder / specified substance detector 9 via the water supply pipe 10 to measure and record the concentration of each substance. The remaining part of the pumped groundwater is sent as it is to the waterfall tower 12 through the pumping pipe 11, where the volatile gas is volatilized in the waterfall tower, and when it exceeds the allowable concentration, it is passed through the repair device and allowed. Release after confirming that the concentration is below the concentration.

【0025】13は前記瀑気塔12から連管14を経て設置す
る濾過槽で、ここで特定物質を吸着濾過する。この濾過
槽を通過した水は送出管18から戻り管19を経て再び前記
記録機兼特定物質検出機9に送られ、各物質毎の濃度を
再測定,記録するが、その後再び逆戻り管20を経て送出
管18に送られる。
Reference numeral 13 is a filtration tank installed from the water vapor tower 12 through a connecting pipe 14 for adsorbing and filtering a specific substance. The water that has passed through this filtration tank is sent from the delivery pipe 18 through the return pipe 19 to the recorder / specified substance detector 9 again, and the concentration of each substance is measured again and recorded. It is then sent to the delivery pipe 18.

【0026】その濃度が、予定した各物質の許容濃度値
のすべてよりも低い値になったときは、逆戻り管20を経
た水をバルブ15を切換え開口して注水管16に送り、ここ
から利用目的に応じた場所に送水する。
When the concentration becomes lower than all the allowed concentration values of each substance planned, the water passing through the return pipe 20 is sent to the water injection pipe 16 by switching the valve 15 and opening it. Deliver water to a place suitable for the purpose.

【0027】また、もし1つ以上の物質が許容濃度を超
えたときは、バルブ15を切換えて排水管17からトレンチ
1内に戻し、上記した作用を循環して行う。
If one or more substances exceed the permissible concentration, the valve 15 is switched to return from the drain pipe 17 to the inside of the trench 1 and the above-described action is circulated.

【0028】[0028]

【発明の効果】本発明は以上のような構成及び作用を有
するものであるため、従来の方法及び装置に比して次の
ような効果を発揮するのである。
Since the present invention has the above-mentioned structure and operation, it exhibits the following effects as compared with the conventional method and apparatus.

【0029】第1に、自然の地下水流量の把握機能が向
上する。即ち、従来法では地下水位又は動水勾配の値を
指標としてダルシー理論から地下水流量を想定している
が、地下水位の上昇期や下降期の地下水位の変動速度は
不飽和層の含水量で大幅な変化を受け、流量との相関を
大幅に乱す欠点をもつところ、本発明の方法は、揚水水
位を一定に保つように揚水量をコントロールすることが
できるから、その揚水量は地下水流量に比例したものと
なる。
First, the function of grasping the natural groundwater flow rate is improved. That is, in the conventional method, the groundwater flow rate is assumed from the Darcy theory using the value of the groundwater level or hydraulic gradient as an index, but the fluctuation rate of the groundwater level during the rising and falling periods of the groundwater level depends on the water content of the unsaturated layer. Since the method of the present invention can control the pumping amount so as to keep the pumping water level constant, the pumping amount is controlled by the groundwater flow rate. It will be proportional.

【0030】第2に、地下水量に含む特定物質の把握率
が向上する。即ち、従来法では観測井によって僅か数セ
ンチから10数センチの横幅の流れを補集するに過ぎない
が、本発明の方法では幅数メートル〜10数メートルの流
れの全断面を補集することができるから、帯水層内で部
分的に散在する水みち流を完全に補集できる。
Secondly, the rate of grasping the specific substance contained in the groundwater amount is improved. That is, in the conventional method, the flow having a width of only several centimeters to ten and several centimeters is collected by the observation well, but the method of the present invention collects the entire cross section of the flow having a width of several meters to ten and several meters. Therefore, it is possible to completely collect the water flow that is partially scattered in the aquifer.

【0031】トレンチの他側面部と下流面部を不透水性
の構造にし、底面部に溝を設け、かつトレンチ内の地下
水位を周辺の地下水位より低くしてあるから、トレンチ
に流入した特定物質は下流側へは全く流出しない。
Since the other side surface portion and the downstream surface portion of the trench are made impermeable, a groove is provided at the bottom portion, and the groundwater level in the trench is set lower than the surrounding groundwater level, the specific substance flowing into the trench Does not flow to the downstream side at all.

【0032】トレンチの底面部に傾斜をもたせて集水溝
を深くし、集水溝の底部の水を揚水する機構であるか
ら、比重が水より重い特定物資も、トレンチ内に停滞す
ることなく揚水することができる。
Since the bottom of the trench is inclined, the water collecting groove is deepened and the water at the bottom of the water collecting groove is pumped up. Therefore, even a specific material having a specific gravity higher than that of water does not stagnate in the trench. Can be pumped.

【0033】第3に、揚水効率が向上する。即ち、従来
の井戸からの揚水法では、特定物質の除去に関係しない
自然条件で流れない停滞水を大量に引き込み、また井戸
周辺に上方向への水みちを発達させて浅層部の地下水を
引き込んでしまうし、停滞水の大量な引き込みでは地盤
沈下を引き起こすことになるのに対し、自然水位の最低
値よりも僅かに低い揚水水位で揚水する本発明の方法で
は、停滞水の引き込みや上方向への水みちの発達はほと
んど無視できるものとなり、地盤沈下現象は全く起らな
い。
Thirdly, the pumping efficiency is improved. That is, the conventional method of pumping water from a well draws in a large amount of stagnant water that does not flow under natural conditions that are not related to the removal of specific substances, and also develops upward water channels around the well to remove groundwater in the shallow layer. In contrast to the fact that a large amount of stagnant water will cause ground subsidence, the method of the present invention in which the pumping water level is slightly lower than the minimum natural water level causes The development of water paths in the direction becomes almost negligible, and the ground subsidence phenomenon does not occur at all.

【0034】第4に、流量と特定物質濃度の監視機能が
向上する。即ち、従来法では一般に間欠的に行なわれる
水位測定や試水の濃度分析に止まるから、間欠部の状態
を把握できないのに対し、本発明の方法ではこれらをほ
ぼ連続的に詳しく知ることができるようになる。
Fourth, the function of monitoring the flow rate and the concentration of the specific substance is improved. That is, in the conventional method, water level measurement and sample water concentration analysis, which are generally performed intermittently, are limited, so that the state of the intermittent portion cannot be grasped, whereas in the method of the present invention, these can be known in almost continuous detail. Like

【0035】第5に、特定物質の除染機能が連続的に自
動化する。即ち、従来法では特定の時期に除染をするに
止まり、残りの期間は放置していたのに対し、本発明の
方法では連続的に除染し、かつ除染効果を連続的に測定
し、その結果と許容濃度との比較から、その後の処理水
の対処を自動的に定めることができるようになる。
Fifth, the decontamination function for specific substances is continuously automated. That is, in the conventional method, decontamination was only performed at a specific time, and the remaining period was left alone, whereas in the method of the present invention, decontamination is continuously performed, and the decontamination effect is continuously measured. From the comparison between the result and the permissible concentration, it becomes possible to automatically determine the subsequent treatment of the treated water.

【0036】したがって、特定物質の除染を省力的にか
つ連続して行うことができるばかりでなく、トレンチ下
流部側への特定物質の流去を完全に遮断することができ
る。また、トレンチの施工では、その下流部側で流れを
生じなくなった範囲にある特定物質を下流部側に流動さ
せることを阻止できるようになる。
Therefore, not only the decontamination of the specific substance can be performed labor-savingly and continuously, but also the outflow of the specific substance to the downstream side of the trench can be completely blocked. Further, in the construction of the trench, it becomes possible to prevent the specific substance in the range where the flow does not occur on the downstream side from flowing to the downstream side.

【図面の簡単な説明】[Brief description of drawings]

【図1】全体設備の正断面図[Fig. 1] Front sectional view of the entire equipment

【図2】図1要部の側断面図FIG. 2 is a side sectional view of the main part of FIG.

【符号の説明】[Explanation of symbols]

1 トレンチ 2 スクリーン部 3 トレンチの底面部 4 集水溝 5 傾斜面部 8 水位センサー 9 記録機兼特定物質検出機 12 瀑気塔 13 濾過槽 15 バルブ 16 注水管 17 排水管 18 送出管 19 戻り管 20 逆戻り管 1 trench 2 screen part 3 bottom part of trench 4 water collection groove 5 inclined surface part 8 water level sensor 9 recorder and specific substance detector 12 waterfall tower 13 filter tank 15 valve 16 water injection pipe 17 drainage pipe 18 delivery pipe 19 return pipe 20 Return pipe

─────────────────────────────────────────────────────
─────────────────────────────────────────────────── ───

【手続補正書】[Procedure amendment]

【提出日】平成4年6月25日[Submission date] June 25, 1992

【手続補正1】[Procedure Amendment 1]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0005[Correction target item name] 0005

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0005】従来の汚染物質のような特定水質を集す
る方法は、前述した観測井又は同じ構造で大口径の新設
井から揚水し、揚水中の特定水質を集する方法を用い
ている。
[0005] Methods of collecting capturing a certain quality, such as a conventional pollutants uses a method in which pumping from new wells of large diameter at observation wells or the same structure described above, the current capturing a certain quality in the pumping ..

【手続補正2】[Procedure Amendment 2]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0006[Correction target item name] 0006

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0006】しかし、揚水による井内水位の低下で
範囲を広げても、循環水流の有効な集幅は数メートル
台に止まってしまい、また揚水中には自然の帯水層内で
停滞水であった水の引き抜きや、揚水で井戸周辺から上
方に発達していく水みちを通るより浅層からの地下水の
引き込み水等が大量に混入される。これらの混入は揚水
中の特定物質の濃度を低めて回収効率を悪くし、不必要
な揚水を大量に生じ、井戸周辺では地盤沈下を引き起こ
す。さらに、揚水時以外に流れている特定物質を集で
きない等の課題があった。
[0006] However, even if spread the catching collection range in the decline of Iuchi water level by pumping, effective catching Atsumarihaba of circulating water flow will stop a few meters stand, also stagnation in the nature of the aquifer in during the pumping A large amount of water is drawn in, and groundwater is drawn in from a shallower layer that passes through the waterway that grows upward from the well area by pumping. These contaminants lower the concentration of specific substances in the pumped water, reduce the collection efficiency, generate a large amount of unnecessary pumped water, and cause ground subsidence around the well. Furthermore, there is a problem such that can not collecting capturing a specific substance flowing except during pumping.

【手続補正3】[Procedure 3]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0008[Correction target item name] 0008

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0008】[0008]

【発明が解決しようとする課題】そこで、本発明は、集
水断面を大幅に広くすることによって帯水層内の水みち
流をより確実に把握し、かつ特定物質の集効率を高め
るようにする。
Therefore [0007] The present invention provides water collecting section more surely grasp the water conducting flow aquifer in by significantly wider, and to enhance the collection efficiency of a specific substance To

【手続補正4】[Procedure amendment 4]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0023[Name of item to be corrected] 0023

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0023】この地下水位は、周辺の自然水位の最低値
よりもやや低い値にすることを原則とするが、地下水
経年変化が大きい時や、特定物質の流入量が異常に多
い時などには、任意の水位に設定し直すことができる機
能をセンサーにもたせるようにする。
[0023] The underground water level, but as a rule to be slightly lower value than the lowest value of the natural water level of the peripheral, underground water level
When there is a large change over time, or when the inflow of a specific substance is abnormally large, the sensor should have a function that allows it to be reset to an arbitrary water level.

【手続補正5】[Procedure Amendment 5]

【補正対象書類名】明細書[Document name to be amended] Statement

【補正対象項目名】0030[Name of item to be corrected] 0030

【補正方法】変更[Correction method] Change

【補正内容】[Correction content]

【0030】第2に、地下水量に含む特定物質の把握率
が向上する。即ち、従来法では観測井によって僅か数セ
ンチから10数センチの横幅の流れを集するに過ぎな
いが、本発明の方法では幅数メートル〜10数メートル
の流れの全断面を集することができるから、帯水層内
で部分的に散在する水みち流を完全に集できる。
Secondly, the rate of grasping the specific substance contained in the groundwater amount is improved. That is, in the conventional method is merely capturing current flow width of 10 centimeters from only a few centimeters by the observation well, the method of the present invention to current capturing the entire cross-section of the flow of a width of several meters to 10 meters that since it is, the water conducting flow partially interspersed aquifer in completely capturing collection.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 地下水の流量及び汚染物等の特定の要監
視物質の濃度を連続的に監視するとともに要監視物質を
自動的に除去することを特徴とする方法。
1. A method comprising continuously monitoring the flow rate of groundwater and the concentration of a specific substance to be monitored such as pollutants and automatically removing the substance to be monitored.
【請求項2】 帯水層又は及び不飽和層の上流側にスク
リーンを設けたほぼ直方体状のトレンチを設置し、この
トレンチの底面部の一部には集水溝を設け、前記底面部
は集水溝方向に傾斜するとともに下流側に傾斜して成
り、前記集水溝には吸込口を設けるとともにこの吸込口
に連設するポンプから地上に設置した記録機兼特定物質
検出機及び瀑気塔に送水管を配設し、この瀑気塔から濾
過槽に連管を配設し、この濾過槽下の送出管に前記記録
機兼特定物質検出機に連結する往復管を配設し、前記送
出管に設けたバルブに地上適所に流出する注水管と再び
地下のトレンチに戻す排水管とを連設して成る装置。
2. A substantially rectangular parallelepiped trench provided with a screen is provided on the upstream side of the aquifer or the unsaturated layer, and a water collecting groove is provided in a part of the bottom of the trench, and the bottom is It is inclined toward the water collection groove and inclined toward the downstream side.The water collection groove is provided with a suction port and a pump connected to this suction port is connected to the recording machine and the specified substance detector and the waterfall installed on the ground. A water supply pipe is arranged in the tower, a connecting pipe is arranged in the filtration tank from the waterfall tower, and a reciprocating pipe connected to the recording machine and the specific substance detector is arranged in the delivery pipe under the filtration tank. A device in which a valve provided in the delivery pipe is connected to a water injection pipe that flows out to a proper place on the ground and a drain pipe that returns to the underground trench again.
JP15014092A 1992-05-19 1992-05-19 Equipment for monitoring and decontaminating groundwater flow rate and specific water quality Expired - Lifetime JP2559654B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15014092A JP2559654B2 (en) 1992-05-19 1992-05-19 Equipment for monitoring and decontaminating groundwater flow rate and specific water quality

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15014092A JP2559654B2 (en) 1992-05-19 1992-05-19 Equipment for monitoring and decontaminating groundwater flow rate and specific water quality

Publications (2)

Publication Number Publication Date
JPH05323040A true JPH05323040A (en) 1993-12-07
JP2559654B2 JP2559654B2 (en) 1996-12-04

Family

ID=15490371

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15014092A Expired - Lifetime JP2559654B2 (en) 1992-05-19 1992-05-19 Equipment for monitoring and decontaminating groundwater flow rate and specific water quality

Country Status (1)

Country Link
JP (1) JP2559654B2 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100714198B1 (en) * 1999-03-01 2007-05-02 페어차일드 세미컨덕터 코포레이션 Mos-gated device having a buried gate and process for forming same
JP2007183160A (en) * 2006-01-06 2007-07-19 Sumiko Consultant Kk Device for observing gas-liquid mixed fluid in the ground
CN113461184A (en) * 2021-08-09 2021-10-01 中国电建集团贵阳勘测设计研究院有限公司 Water body pollution treatment system based on real-time hydrology monitoring data

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100714198B1 (en) * 1999-03-01 2007-05-02 페어차일드 세미컨덕터 코포레이션 Mos-gated device having a buried gate and process for forming same
JP2007183160A (en) * 2006-01-06 2007-07-19 Sumiko Consultant Kk Device for observing gas-liquid mixed fluid in the ground
CN113461184A (en) * 2021-08-09 2021-10-01 中国电建集团贵阳勘测设计研究院有限公司 Water body pollution treatment system based on real-time hydrology monitoring data

Also Published As

Publication number Publication date
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