JPH0623210A - Method and device for detecting suspension concentration - Google Patents

Method and device for detecting suspension concentration

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Publication number
JPH0623210A
JPH0623210A JP22318292A JP22318292A JPH0623210A JP H0623210 A JPH0623210 A JP H0623210A JP 22318292 A JP22318292 A JP 22318292A JP 22318292 A JP22318292 A JP 22318292A JP H0623210 A JPH0623210 A JP H0623210A
Authority
JP
Japan
Prior art keywords
suspension
pipe
concentration
water
water level
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.)
Pending
Application number
JP22318292A
Other languages
Japanese (ja)
Inventor
Tadashi Takai
規 高井
Isao Takayama
功 高山
Yoshikazu Oshima
美一 大島
Yukio Nagai
之雄 永井
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.)
Inax Corp
Original Assignee
Inax Corp
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 Inax Corp filed Critical Inax Corp
Priority to JP22318292A priority Critical patent/JPH0623210A/en
Publication of JPH0623210A publication Critical patent/JPH0623210A/en
Pending legal-status Critical Current

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  • Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)

Abstract

PURPOSE:To accurately and automatically detect the concentration of a suspension by inserting a pipe into a suspension storing vessel (reaction vessel), precipitating particles in the pipe to turn the suspension into clear water and detecting the difference in water level between the surface of the clear water and that of the suspension in the storing vessel to detect the concentration of the suspension. CONSTITUTION:A pipe 9 is inserted into a reaction vessel 3 and immersed in a suspension. Particles gradually precipitate with the lapse of time from the suspension in the pipe 9 which is turned into clear water. As a result, the difference in specific gravity occurs between the clear water in the pipe 9 and the suspension in the reaction vessel 3 outside the pipe 9, causing the clear water in the pipe 9 to be pushed up by the suspension, permitting the surface of the clear water to be raised higher than that of the suspension in the reaction vessel 3. The difference in water level varies in proportion to the difference in the specific gravity based on the difference in the concentration of the suspension. Therefore, by detecting the difference of water level, the concentration of the suspension is detected.

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、工場排水等を処理する
水処理装置において、工場排水の濃度を自動的に検出す
る方法と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 automatically detecting the concentration of factory wastewater in a water treatment apparatus for treating factory wastewater and the like.

【0002】[0002]

【従来の技術】従来において、例えば、便器や手洗器,
洗面器等の衛生陶器を製造する工場やタイル工場等の釉
薬を取り扱う工場等においては、釉薬を含んだ懸濁液の
工場排水が排出される。この工場排水は、そのまま下水
等へ排出することはできず、浄化処理することが必要で
ある。
2. Description of the Related Art Conventionally, for example,
In a factory that manufactures sanitary ware such as washbasins and a factory that handles glazes such as a tile factory, factory wastewater of a suspension containing glaze is discharged. This factory effluent cannot be discharged as it is to sewage, etc., and must be purified.

【0003】図3は、従来の釉薬を含んだ懸濁液の工場
排水を処理する装置の全体を示すシステム図である。同
図に示すように、この従来装置では、先ず釉薬を含んだ
懸濁液の工場排水を一旦原水槽1へ貯溜し、これを揚水
ポンプ2で反応槽3へ汲み上げている。反応槽3では、
ポリ塩化アルミニウム等の凝集剤を投入している。凝集
剤は、後述する沈殿槽5において、懸濁液の粒子の凝集
を促進させ、水処理効率を良くするためのものである。
FIG. 3 is a system diagram showing an entire apparatus for treating industrial wastewater of a conventional suspension containing glaze. As shown in the figure, in this conventional apparatus, first, factory wastewater of a suspension containing glaze is temporarily stored in a raw water tank 1 and then pumped up by a pump 2 to a reaction tank 3. In the reaction tank 3,
A flocculant such as polyaluminum chloride is added. The coagulant is for promoting coagulation of particles of the suspension in the settling tank 5 described later to improve water treatment efficiency.

【0004】ところで、凝集剤を投入すると、懸濁液は
酸性になる。そのため、pH調整が必要であり、この従
来装置では次の反応槽4でNaOHを投入してpH調整
を行っている。そして、最後に沈殿槽5で懸濁液の粒子
を沈殿させ、上方の清水のみを取り出して下水等へ排水
している。
By the way, when the coagulant is added, the suspension becomes acidic. Therefore, it is necessary to adjust the pH, and in this conventional apparatus, pH is adjusted by adding NaOH in the next reaction tank 4. Then, finally, the particles of the suspension are settled in the settling tank 5, and only fresh water above is taken out and discharged to sewage or the like.

【0005】而して、効率良く水処理するためには、反
応槽3においてその流入量が一定であるとすると、原水
槽1から汲み上げられて来る工場排水の濃度に応じた量
の凝集剤を投入する必要がある。然しながら、工場排水
の濃度が高濃度である場合には、反応槽3へ投入できる
凝集剤の限界量を越える場合があり、通常の処理が行え
なくなる虞れがある。
In order to treat water efficiently, assuming that the inflow rate is constant in the reaction tank 3, an amount of coagulant corresponding to the concentration of the factory wastewater pumped from the raw water tank 1 is used. Need to throw in. However, if the concentration of the factory wastewater is high, the limit amount of the coagulant that can be added to the reaction tank 3 may be exceeded, and normal treatment may not be performed.

【0006】そのため、従来にあっては、反応槽3にお
いて凝集剤を投入できる量を越えた高濃度の工場排水が
流入した場合には、揚水ポンプ2で汲み上げられた工場
排水を逃がし弁6を開操作して戻り管路7から原水槽1
へ還流させ、反応槽3へ流入する工場排水の量を減らし
て凝集剤と懸濁液との好適な反応が得られるようにして
いる。
Therefore, in the prior art, when a high-concentration factory wastewater in excess of the amount in which the coagulant can be charged flows into the reaction tank 3, the factory wastewater pumped up by the pumping pump 2 is allowed to flow through the relief valve 6. Open operation and return pipe 7 to raw water tank 1
To reduce the amount of factory wastewater flowing into the reaction tank 3 so that a suitable reaction between the flocculant and the suspension can be obtained.

【0007】また従来の別な方法としては、原水槽1を
大型化し、工場排水の濃度の影響が少なくなるように平
均化する場合もある。なお、図3において、8は反応槽
3内に設置した撹拌羽根である。
As another conventional method, the raw water tank 1 may be enlarged and averaged so that the influence of the concentration of factory wastewater is reduced. In FIG. 3, 8 is a stirring blade installed in the reaction tank 3.

【0008】[0008]

【発明が解決しようとする課題】このように従来の水処
理装置では、反応槽3で投入できる凝集剤の量を越えた
高濃度の工場排水の場合には、その流量を減らすべく、
逃がし弁6を操作して反応槽3へ流入する工場排水の量
を調整している。然しながら、前記逃がし弁6の開閉操
作による流量調整は、作業員が反応槽3における状態を
経験則に基づいて目視により確認しながら行わなければ
ならず、監視員を常時配置しておかねばならず、不正確
であり、非能率的でもあった。また従来の原水槽1を大
型化する対策の場合には、この大型化に伴って設備費用
の高騰や広い設置スペースが必要である等の問題があ
り、あまり一般的ではなかった。
As described above, in the conventional water treatment apparatus, in the case of high-concentration factory wastewater exceeding the amount of coagulant that can be charged in the reaction tank 3, the flow rate of the wastewater should be reduced.
The relief valve 6 is operated to adjust the amount of factory wastewater flowing into the reaction tank 3. However, the flow rate adjustment by the opening / closing operation of the relief valve 6 must be performed while the operator visually confirms the state of the reaction tank 3 based on an empirical rule, and a supervisor must always be arranged. It was also inaccurate and inefficient. Further, in the case of the conventional measures for increasing the size of the raw water tank 1, there are problems such as soaring equipment costs and a large installation space accompanying the increase in size, which is not so common.

【0009】なお、反応槽3内の工場排水の濃度を検出
する手段としては、赤外線センサー等の透過型の光セン
サーを用い、赤外線の透過量を測定することにより検知
する手段やフロートを用いた比重計を用いて検出する手
段があり、これらの検知手段による出力信号に基づいて
揚水ポンプ2の回転数を制御し、凝集剤との好適な反応
促進を図るようにすることも考えられる。
As the means for detecting the concentration of the factory wastewater in the reaction tank 3, a transmissive optical sensor such as an infrared sensor is used, and a means for detecting by measuring the amount of transmitted infrared rays or a float is used. There is a means for detecting using a hydrometer, and it is conceivable to control the rotation speed of the pumping pump 2 based on the output signals from these detecting means so as to promote a suitable reaction with the coagulant.

【0010】然しながら、透過型の光センサーを用いる
場合は、工場排水の懸濁液の粒子がセンサーに付着し、
濃度に対応した正確な透過量が得られなくなるという欠
点があり、採用できないでいた。またフロートを用いた
比重計を用いる方法でも、やはりフロートに懸濁液の粒
子が付着し、正確な濃度検出が得られなくなり、採用で
きないでいた。そのため、従来では作業員が経験則に基
づいて目視により反応槽3の状態を確認しながら、逃が
し弁6を開閉制御することにより、反応槽3内で工場排
水と凝集剤とを反応させざるを得ず、上述した欠点を有
するものであった。
However, when a transmissive optical sensor is used, the particles of the suspension of factory wastewater adhere to the sensor,
It cannot be adopted because it has a drawback that an accurate transmission amount corresponding to the concentration cannot be obtained. Further, even in the method using a hydrometer using a float, particles of the suspension adhere to the float and accurate concentration detection cannot be obtained. Therefore, conventionally, an operator must check the state of the reaction tank 3 based on an empirical rule and control the opening / closing of the relief valve 6 to react the factory wastewater with the coagulant in the reaction tank 3. It was not obtained, and it had the above-mentioned fault.

【0011】また揚水ポンプ2は、駆動スイッチをON
にしたまま常時、一定した回転数を以て運転している。
そのため、原水槽1の水面高さにより、揚水ポンプ2の
吸い込み口での水圧が変化し、汲み上げ量の変化となっ
て、反応槽3へ適切な量の工場排水を供給できないとい
う欠点があった。更に、この揚水ポンプ2の汲み上げ量
の変化は、揚水ポンプ2のストレーナ部分へのゴミのつ
まり具合によっても影響を受けるものであった。
The pumping pump 2 has a drive switch turned on.
It is always operated with a constant number of revolutions while it is kept at.
Therefore, there is a drawback that the water pressure at the suction port of the pumping pump 2 changes depending on the water level of the raw water tank 1 and the pumping amount changes, so that an appropriate amount of factory wastewater cannot be supplied to the reaction tank 3. . Further, the change in the pumping amount of the pump 2 is also affected by the degree of dust clogging the strainer portion of the pump 2.

【0012】[0012]

【課題を解決するための手段】本発明は従来の前記課題
に鑑みてこれを改良除去したものであって、反応槽での
懸濁液の濃度検出を自動的に行い、これにより原水槽か
ら反応槽へ供給される懸濁液の流量を制御し、水処理シ
ステムの全体を自動化できる方法及び装置を提供せんと
するものである。
SUMMARY OF THE INVENTION The present invention has been made by improving the above-mentioned problems in view of the above-mentioned conventional problems, and automatically detects the concentration of a suspension in a reaction tank, and It is an object of the present invention to provide a method and an apparatus capable of controlling the flow rate of a suspension supplied to a reaction tank and automating an entire water treatment system.

【0013】而して、前記課題を解決するために本発明
が採用した方法は、懸濁液の貯溜槽の中へパイプを挿入
し、パイプ内の粒子を沈降させて清水とし、該清水の水
面と貯溜槽内の懸濁液の水面との水位差を検出すること
で懸濁液の濃度を検出するようにしたことを特徴とする
懸濁液濃度検出方法である。
Thus, the method adopted by the present invention to solve the above-mentioned problems is to insert a pipe into a suspension storage tank, to settle particles in the pipe into fresh water, and to obtain the fresh water. The suspension concentration detecting method is characterized in that the concentration of the suspension is detected by detecting a water level difference between the water surface and the water surface of the suspension in the storage tank.

【0014】また本発明が採用した装置は、懸濁液の貯
溜槽へ挿入されたパイプ中に設けた内パイプの上端側を
密閉し、該密閉室をダイヤフラム式等の圧力検知器へ連
通接続し、圧力検出器の出力信号からパイプ内の清水の
水面と貯溜槽内の懸濁液の水面との水位差を求めて懸濁
液の濃度を検出する濃度検出器を設けたことを特徴とす
る懸濁液濃度検出装置である。
In the apparatus adopted by the present invention, the upper end side of the inner pipe provided in the pipe inserted into the suspension storage tank is closed, and the closed chamber is connected to a pressure detector of a diaphragm type or the like. However, a concentration detector for detecting the concentration of the suspension by determining the water level difference between the surface of the fresh water in the pipe and the surface of the suspension in the storage tank from the output signal of the pressure detector is characterized by being provided. This is a suspension concentration detecting device.

【0015】[0015]

【作用】本発明の濃度検出方法は、貯溜槽(原水槽また
は反応槽等)内へパイプを挿入し、懸濁液の中へ浸漬し
ている。パイプ内の懸濁液は、時間の経過と共に次第に
粒子が沈降し、パイプ内は清水となる。そのため、パイ
プ内の清水と、パイプ外の貯溜槽内の懸濁液との間に比
重差が発生し、パイプ内の清水は懸濁液に押し上げられ
てその水面が貯溜槽内の懸濁液水面よりも上昇するよう
になる。この水位差は、懸濁液の濃度差に基づく比重差
に比例して変化するものである。それ故、水位差を検出
することにより懸濁液の濃度を検知することが可能であ
る。
In the concentration detecting method of the present invention, a pipe is inserted into a storage tank (raw water tank, reaction tank, etc.) and immersed in a suspension. In the suspension in the pipe, particles gradually settle with the passage of time, and the pipe becomes clear water. As a result, a specific gravity difference occurs between the fresh water inside the pipe and the suspension inside the storage tank outside the pipe, and the fresh water inside the pipe is pushed up by the suspension so that its water surface is the suspension inside the storage tank. It will rise above the water level. This difference in water level changes in proportion to the difference in specific gravity based on the difference in concentration of the suspension. Therefore, it is possible to detect the concentration of the suspension by detecting the water level difference.

【0016】本発明の濃度検出装置は、前記水位差を検
出する手段として、貯溜槽内へ挿入したパイプ中に設け
た内パイプの上端側を密閉し、該密閉室をダイヤフラム
式等の圧力検知器へ連通接続している。これによれば、
水位差は圧力の変動として取り出されるため、前記密閉
室の圧力を検出することで、水位差を検知することが可
能である。
In the concentration detecting device of the present invention, as means for detecting the water level difference, the upper end side of the inner pipe provided in the pipe inserted into the storage tank is hermetically sealed, and the hermetic chamber is pressure-sensing by a diaphragm type or the like. Connected to the vessel. According to this
Since the water level difference is taken out as a change in pressure, it is possible to detect the water level difference by detecting the pressure in the closed chamber.

【0017】[0017]

【実施例】以下に、本発明の濃度検出方法及び装置を、
釉薬を含んだ工場排水を処理する場合の実施例に基づい
て図面を参照して説明すると次の通りである。なお、従
来の場合と同一符号は同一部材である。
EXAMPLES The concentration detection method and apparatus of the present invention will be described below.
The following is a description with reference to the drawings on the basis of an example of treating factory wastewater containing a glaze. The same reference numerals as in the conventional case are the same members.

【0018】図1は本発明の濃度検出方法の原理を説明
する反応槽3の縦断面図である。同図に示すように、本
発明方法にあっては、反応槽3の懸濁液の中へパイプ9
を挿入している。このパイプ9を挿入することにより、
パイプ9内の懸濁液の粒子は時間が経過するに伴って沈
降し、パイプ9内は清水となる。そのため、パイプ9の
外の反応槽3内の懸濁液との間で濃度差に基づく比重差
を発生し、パイプ9内の清水は懸濁液に押し上げられ水
位差を発生するようになる。従って、この水位差を検出
することにより、反応槽3内における懸濁液の濃度を検
出することが可能である。
FIG. 1 is a vertical sectional view of a reaction tank 3 for explaining the principle of the concentration detecting method of the present invention. As shown in the figure, in the method of the present invention, the pipe 9 is inserted into the suspension in the reaction tank 3.
Have been inserted. By inserting this pipe 9,
The particles of the suspension in the pipe 9 settle down as time passes, and the pipe 9 becomes clean water. Therefore, a specific gravity difference based on the concentration difference is generated between the pipe 9 and the suspension in the reaction tank 3, and the fresh water in the pipe 9 is pushed up by the suspension to cause a water level difference. Therefore, by detecting this water level difference, it is possible to detect the concentration of the suspension in the reaction tank 3.

【0019】例えば、直径が100mmで長さが100
0mmのパイプを反応槽3内へ浸漬し、水温が20℃の
ときの水の比重が0.997で、釉薬を含んだ懸濁液の
粒子の真比重が2.65であるときの、懸濁液の濃度
と、懸濁液の比重と、水位差との関係は次の通りであ
る。すなわち、濃度が0%のときの懸濁液比重は0.9
97で水位差は0mmであり、濃度0.1%のときの懸
濁液比重は0.9976で水位差は0.60mmであ
り、濃度0.2%のときの懸濁液比重は0.9982で
水位差は1.20mmであり、濃度0.5%のときの懸
濁液比重は1.0001で水位差は3.10mmであ
り、濃度が1.0%のときの懸濁液比重は1.0033
で水位差は6.28mmであり、濃度2.0%のときの
懸濁液比重は1.0096で水位差は12.48mmで
あり、濃度5.0%のときの懸濁液比重は1.0291
で水位差は31.19mmであった。
For example, a diameter of 100 mm and a length of 100
When a 0 mm pipe is immersed in the reaction tank 3, the specific gravity of water when the water temperature is 20 ° C. is 0.997, and the true specific gravity of the particles of the suspension containing the glaze is 2.65. The relationship among the concentration of the suspension, the specific gravity of the suspension, and the water level difference is as follows. That is, the specific gravity of the suspension when the concentration is 0% is 0.9
97, the water level difference was 0 mm, the suspension specific gravity at a concentration of 0.1% was 0.9976, the water level difference was 0.60 mm, and the suspension specific gravity at a concentration of 0.2% was 0. 9982, the water level difference is 1.20 mm, the suspension specific gravity at a concentration of 0.5% is 1.0001, the water level difference is 3.10 mm, and the suspension specific gravity at a concentration of 1.0%. Is 1.0033
The water level difference is 6.28 mm, the suspension specific gravity at a concentration of 2.0% is 1.0096 and the water level difference is 12.48 mm, and the suspension specific gravity at a concentration of 5.0% is 1 .0291
The water level difference was 31.19 mm.

【0020】図2は、前記濃度差を検出する原理に基づ
いて釉薬を含んだ工場排水を処理する装置へ本発明を適
用した場合の全体を示すシステム図である。同図に示す
ように、この実施例にあっては、反応槽3内へ直径が1
00mmのパイプ9を挿入し、該パイプ9の上端側にソ
ケット10を介して直径が75mmの内パイプ11スラ
イド自在に嵌合装着し、内パイプ11の内部に密閉室1
2を形成している。なお、パイプ9内は大気と連通して
いる必要があるので、通気孔(開放口)17が必要であ
る。
FIG. 2 is a system diagram showing the whole of the case where the present invention is applied to an apparatus for treating factory wastewater containing glaze based on the principle of detecting the concentration difference. As shown in the figure, in this embodiment, a diameter of 1
A 00 mm pipe 9 is inserted, an inner pipe 11 having a diameter of 75 mm is slidably fitted and mounted on an upper end side of the pipe 9 through a socket 10, and the closed chamber 1 is provided inside the inner pipe 11.
Forming 2. Since the inside of the pipe 9 needs to communicate with the atmosphere, a vent hole (opening port) 17 is required.

【0021】そして、密閉室12を形成する内パイプ1
1の上端側を、ホース13でダイヤフラム式の圧力検出
器14へ連通接続している。更に、該圧力検出器14は
その出力信号を電気信号へ変換する変換器15へ接続さ
れ、その出力はインバータ16へ入力されるようになっ
ている。インバータ16は、変換器15の電圧に応じて
これを周波数変換し、反応槽3内の揚水ポンプ2をイン
バータ制御するようにしている。
Then, the inner pipe 1 forming the closed chamber 12
The upper end side of 1 is communicatively connected to a diaphragm type pressure detector 14 by a hose 13. Further, the pressure detector 14 is connected to a converter 15 for converting its output signal into an electric signal, and its output is inputted to an inverter 16. The inverter 16 frequency-converts the voltage of the converter 15 in accordance with the voltage of the converter 15 to control the pumping pump 2 in the reaction tank 3 by an inverter.

【0022】次に、上述の如く構成された水処理システ
ムの動作態様を説明する。先ず、釉薬を含んだ工場排水
の懸濁液は、一旦原水槽1へ貯溜され、揚水ポンプ2に
より反応槽3へ汲み上げられている。而して、本実施例
にあっては、後述する如く、揚水ポンプ2を周波数制御
し、反応槽3で投入されるポリ塩化アルミニウム等の凝
集剤の量に適切に対応すべく工場排水の濃度に応じた流
量を、原水槽2から汲み上げて反応槽3へ供給するよう
にしている。
Next, an operation mode of the water treatment system configured as described above will be described. First, a suspension of factory wastewater containing a glaze is temporarily stored in a raw water tank 1 and then pumped to a reaction tank 3 by a pump 2. Thus, in this embodiment, as described later, the frequency of the pump 2 is controlled so that the concentration of the factory effluent can be adjusted to appropriately correspond to the amount of the coagulant such as polyaluminum chloride charged in the reaction tank 3. A flow rate corresponding to the above is drawn from the raw water tank 2 and supplied to the reaction tank 3.

【0023】反応槽3では、懸濁液内に挿入浸漬された
パイプ9内の清水の水面が、懸濁液の濃度に応じて懸濁
液の水面との間に水位差を発生するようになる。そし
て、この水位差は、内パイプ11の上部側の密閉室12
の圧力変動として圧力検出器14で検出される。圧力検
出器14の出力信号は、変換器15によって電圧信号に
変換され、更にインバータ16に入力される。インバー
タ16は、前記圧力検出器14の出力信号に比例する電
圧信号値に基づいて揚水ポンプ2の回転数を周波数制御
する。
In the reaction tank 3, the water level of the fresh water in the pipe 9 inserted and immersed in the suspension causes a water level difference with the water level of the suspension according to the concentration of the suspension. Become. And, this water level difference is due to the closed chamber 12 on the upper side of the inner pipe 11.
Is detected by the pressure detector 14 as the pressure fluctuation. The output signal of the pressure detector 14 is converted into a voltage signal by the converter 15 and further input to the inverter 16. The inverter 16 frequency-controls the rotation speed of the pumping pump 2 based on the voltage signal value proportional to the output signal of the pressure detector 14.

【0024】従って、揚水ポンプ2は、結果として反応
槽3内の懸濁液の濃度に応じて、その汲み上げ流量をコ
ントロールし、反応槽3へ供給することになる。そのた
め、原水槽1へ流入する工場排水の濃度の変化があった
場合でも、反応槽3へ投入できるポリ塩化アルミニウム
等の凝集剤の最大量に適切に対応すべく、原水槽1から
反応槽3へ供給される排水の量をコントロールでき、反
応槽3内において最も効率良く、懸濁液と凝集剤とを反
応させることができる。つまり、最も効率良い水処理が
可能である。尚、反応槽3以降の水処理については、図
3に示す従来の場合と同じであり、ここでの説明は省略
する。
Therefore, the pumping pump 2 consequently controls the pumping flow rate of the suspension in accordance with the concentration of the suspension in the reaction tank 3 and supplies it to the reaction tank 3. Therefore, even if there is a change in the concentration of the factory effluent flowing into the raw water tank 1, the raw water tank 1 to the reaction tank 3 should be appropriately adjusted to cope with the maximum amount of the coagulant such as polyaluminum chloride that can be added to the reaction tank 3. It is possible to control the amount of waste water supplied to the reactor, and the suspension and the flocculant can be reacted most efficiently in the reaction tank 3. That is, the most efficient water treatment is possible. The water treatment after the reaction tank 3 is the same as the conventional case shown in FIG. 3, and the description thereof is omitted here.

【0025】ところで、本発明は上述した実施例に限定
されるものではなく、適宜の変更が可能である。例え
ば、パイプ9の直径は、反応槽3内において撹拌羽根8
で懸濁液を撹拌してもその影響がパイプ9内へ影響しな
いような大きさのものであればよい。またパイプ9の長
さは、流量や懸濁液の性質に応じて適宜変更するように
すればよい。また圧力検出器14において、エアー漏れ
があったり、排水中に空気の巻き込みがあった場合に
は、タイマーでポンプ電源を30〜60分ごとに20秒
程度OFF動作させて水面を下げることにより、スライ
ド式の内パイプ11を大気へ開放させ、自動ゼロ点調整
を行うようにすればよい。更に、パイプ9内の清水の水
面と懸濁液の水面との水面差は、内パイプ11内におい
て赤外線センサーや超音波センサー,フロート式の水位
計等を用いて行うことも可能である。
By the way, the present invention is not limited to the above-mentioned embodiments, but can be appropriately modified. For example, the diameter of the pipe 9 may be the same as the stirring blade 8 in the reaction tank 3.
Any size may be used as long as the effect does not affect the inside of the pipe 9 even if the suspension is stirred. Further, the length of the pipe 9 may be appropriately changed depending on the flow rate and the property of the suspension. Further, in the pressure detector 14, when there is air leakage or air is trapped in the drainage, the pump power is turned off every 30 to 60 minutes for about 20 seconds by the timer to lower the water surface. The slide type inner pipe 11 may be opened to the atmosphere and the automatic zero point adjustment may be performed. Furthermore, the water level difference between the fresh water surface in the pipe 9 and the water surface of the suspension liquid can be measured in the inner pipe 11 by using an infrared sensor, an ultrasonic sensor, a float type water level gauge, or the like.

【0026】[0026]

【発明の効果】以上説明したように本発明にあっては、
懸濁液内へ挿入浸漬したパイプ内の清水と懸濁液との水
位差を検出することにより、懸濁液の濃度を検出してお
り、極めて容易に且つ正確に懸濁液の濃度を検出するこ
とが可能である。また前記水位差を検出する手段とし
て、内パイプの上端側を密閉し、該密閉室をダイヤフラ
ム式等の圧力検知器へ連通接続し、水位差を密閉室の圧
力変動として取り出し、自動検出するようにしている。
そのため、水処理システムを全自動化することが可能で
あり、監視員を常時配設する等のことが不要となる。
As described above, according to the present invention,
The concentration of the suspension is detected by detecting the water level difference between the fresh water in the pipe inserted and immersed in the suspension and the suspension, and the concentration of the suspension can be detected very easily and accurately. It is possible to Further, as a means for detecting the water level difference, the upper end side of the inner pipe is hermetically sealed, and the hermetically sealed chamber is connected to a pressure detector of a diaphragm type or the like so that the water level difference is taken out as a pressure fluctuation in the hermetically sealed chamber and automatically detected. I have to.
Therefore, it is possible to fully automate the water treatment system, and it is not necessary to constantly arrange a monitoring person.

【0027】また従来のように揚水ポンプを常に一定駆
動させる必要がなく、濃度に応じて揚水ポンプの回転数
を制御することができるようになり、揚水ポンプの消費
電力を大幅に低減させることが可能である。
Further, unlike the conventional case, it is not necessary to constantly drive the pumping pump constantly, and the number of rotations of the pumping pump can be controlled according to the concentration, so that the power consumption of the pumping pump can be greatly reduced. It is possible.

【0028】更に、従来では水処理効率を上げるため
に、凝集剤等の薬液を懸濁液の最高濃度に合わせて投入
しており、濃度が低い場合には無駄になっていたが、本
発明では懸濁液濃度と薬液の量とを適切に対応させるこ
とができ、高価な薬液の使用量を低減させることが可能
である。
Further, in the past, in order to improve the water treatment efficiency, a chemical solution such as a flocculant was added according to the maximum concentration of the suspension, which was wasted when the concentration was low. With, it is possible to appropriately correspond the suspension concentration and the amount of the chemical liquid, and it is possible to reduce the amount of the expensive chemical liquid used.

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

【図1】本発明方法の原理を説明する反応槽の縦断面図
である。
FIG. 1 is a vertical sectional view of a reaction tank for explaining the principle of the method of the present invention.

【図2】本発明に係る水処理装置の全体システム図であ
る。
FIG. 2 is an overall system diagram of a water treatment device according to the present invention.

【図3】従来の水処理装置の全体システム図である。FIG. 3 is an overall system diagram of a conventional water treatment device.

【符号の説明】[Explanation of symbols]

1…原水槽 2…揚水ポンプ 3…反応槽 9…パイプ 10…ソケット 11…スライド式の内パイプ 12…密閉室 14…圧力検出器 15…変換器 16…インバータ 1 ... Raw water tank 2 ... Pumping pump 3 ... Reaction tank 9 ... Pipe 10 ... Socket 11 ... Sliding inner pipe 12 ... Closed chamber 14 ... Pressure detector 15 ... Converter 16 ... Inverter

───────────────────────────────────────────────────── フロントページの続き (72)発明者 永井 之雄 岐阜県恵那郡明智町大田字吉原1125−3 株式会社明智イナックス内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Norio Nagai 1125-3, Yoshihara, Akechi-cho, Ena-gun, Gifu Prefecture Akechi Inax Co., Ltd.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 懸濁液の貯溜槽の中へパイプを挿入し、
パイプ内の粒子を沈降させて清水とし、該清水の水面と
貯溜槽内の懸濁液の水面との水位差を検出することで懸
濁液の濃度を検出するようにしたことを特徴とする懸濁
液濃度検出方法。
1. Inserting a pipe into a suspension reservoir,
It is characterized in that particles in the pipe are settled to form fresh water, and the concentration of the suspension is detected by detecting a water level difference between the surface of the fresh water and the surface of the suspension in the storage tank. Suspension concentration detection method.
【請求項2】 懸濁液の貯溜槽へ挿入されたパイプ中に
設けた内パイプの上端側を密閉し、該密閉室をダイヤフ
ラム式等の圧力検知器へ連通接続し、圧力検出器の出力
信号からパイプ内の清水の水面と貯溜槽内の懸濁液の水
面との水位差を求めて懸濁液の濃度を検出する濃度検出
器を設けたことを特徴とする懸濁液濃度検出装置。
2. An output of a pressure detector, wherein an upper end side of an inner pipe provided in a pipe inserted into a suspension storage tank is closed, and the closed chamber is connected to a pressure detector of a diaphragm type or the like for communication. A suspension concentration detecting device provided with a concentration detector for detecting the concentration of the suspension by obtaining a water level difference between the water surface of the fresh water in the pipe and the water surface of the suspension in the storage tank from the signal. .
JP22318292A 1992-07-08 1992-07-08 Method and device for detecting suspension concentration Pending JPH0623210A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP22318292A JPH0623210A (en) 1992-07-08 1992-07-08 Method and device for detecting suspension concentration

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22318292A JPH0623210A (en) 1992-07-08 1992-07-08 Method and device for detecting suspension concentration

Publications (1)

Publication Number Publication Date
JPH0623210A true JPH0623210A (en) 1994-02-01

Family

ID=16794093

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22318292A Pending JPH0623210A (en) 1992-07-08 1992-07-08 Method and device for detecting suspension concentration

Country Status (1)

Country Link
JP (1) JPH0623210A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08267267A (en) * 1995-03-29 1996-10-15 Mazda Motor Corp Laser beam heat treatment device and method thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5896237A (en) * 1981-12-04 1983-06-08 Nippon Sheet Glass Co Ltd Specific gravity measurement of suspension

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5896237A (en) * 1981-12-04 1983-06-08 Nippon Sheet Glass Co Ltd Specific gravity measurement of suspension

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08267267A (en) * 1995-03-29 1996-10-15 Mazda Motor Corp Laser beam heat treatment device and method thereof

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