JP2002205080A - Dephosphorization method and dephosphorization equipment for orthophosphoric acid-containing water - Google Patents

Dephosphorization method and dephosphorization equipment for orthophosphoric acid-containing water

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Publication number
JP2002205080A
JP2002205080A JP2001003854A JP2001003854A JP2002205080A JP 2002205080 A JP2002205080 A JP 2002205080A JP 2001003854 A JP2001003854 A JP 2001003854A JP 2001003854 A JP2001003854 A JP 2001003854A JP 2002205080 A JP2002205080 A JP 2002205080A
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JP
Japan
Prior art keywords
calcium
concentration
water
treated water
ions
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
JP2001003854A
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Japanese (ja)
Other versions
JP4631169B2 (en
Inventor
Satoshi Ishizuka
諭 石塚
Ichiro Sumita
一郎 住田
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.)
Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Priority to JP2001003854A priority Critical patent/JP4631169B2/en
Publication of JP2002205080A publication Critical patent/JP2002205080A/en
Application granted granted Critical
Publication of JP4631169B2 publication Critical patent/JP4631169B2/en
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Abstract

PROBLEM TO BE SOLVED: To stably obtain treated water of a low phosphorus concentration and high water quality by surely removing the phosphorus in raw water which is drastic in the fluctuation of water quality, such as a calcium concentration, calcium ion concentration and M-alkalinity. SOLUTION: This dephosphorization method comprises measuring the pH and calcium ion concentration in the treated water and adding pH control agents and calcium ions to the raw water in such a manner that the respective measured values attain prescribed values. This dephosphorization equipment reacts the raw water and the calcium ions in reaction chambers 2 and 3 and subjects insoluble matter to a separation of solid from the liquid in a settling tank. The equipment has an arithmetic controller which is inputted with the output signal of pH measuring means 6 for the treated water and the output signal of calcium concentration measuring means 7, computes the pH and calcium concentration to give the prescribed value of the orthophosphoric acid concentration of the treated water from the relation between the pH and the dissolution product of calcium phosphate and outputs the control signal to control the amounts of the pH control agents and the amounts of the calcium ions to be added respectively to pH control agent adding means P3 and calcium adding means P2.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、正リン酸イオンを
含有する原水にカルシウムイオンを添加してリン酸カル
シウムの不溶化物を生成させ、これを分離して処理水を
得る正リン酸含有水の脱リン方法及び脱リン装置に係
り、特に、処理水のpH及びカルシウムイオン濃度に基
いてpH調整剤とカルシウムイオンの添加量を調整する
ことにより、リン濃度やカルシウムイオン濃度、M−ア
ルカリ度等の水質変動が激しい原水中のリンを確実に除
去して、リン濃度の低い高水質の処理水を安定に得る脱
リン方法及び脱リン装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for removing water containing orthophosphoric acid by adding calcium ions to raw water containing orthophosphate ions to form an insolubilized product of calcium phosphate and separating it to obtain treated water. The present invention relates to a phosphorus method and a dephosphorization apparatus, and in particular, by adjusting the addition amount of a pH adjuster and calcium ions based on the pH and calcium ion concentration of treated water, to adjust the phosphorus concentration, calcium ion concentration, M-alkaliness, etc. The present invention relates to a dephosphorization method and a dephosphorization device for reliably removing phosphorus in raw water in which water quality fluctuates greatly and stably obtaining high-quality treated water having a low phosphorus concentration.

【0002】[0002]

【従来の技術】下水、し尿、排水等の嫌気、好気処理工
程で発生する汚泥脱水濾液、消化脱離液等の正リン酸イ
オンを含有する原水からリンを除去する方法として、原
水にカルシウムイオンを添加して、pHアルカリ性でリ
ン酸カルシウムの不溶化物を生成させ、これを分離する
ことによりリンを除去する方法がある。この方法で用い
られるカルシウムイオン源としては、水酸化カルシウム
(Ca(OH))、塩化カルシウム(CaCl)等
があり、このうち、Ca(OH)を用いた場合には、
pH調整のためのアルカリ剤を兼用することができる。
CaClを用いた場合には、別途、水酸化ナトリウム
(NaOH)等のアルカリを添加してpH調整を行う。
また、反応形態としては、反応槽で原水にカルシウム化
合物と必要に応じてアルカリ剤を添加して反応させ、不
溶化物を沈殿槽で分離する沈殿法と、原水を晶折槽に導
入して種晶の表面にリン酸カルシウムを析出させる晶折
法とがある。
2. Description of the Related Art As a method for removing phosphorus from raw water containing orthophosphate ions, such as sludge dewatered filtrate and digestion desorbed liquid generated in anaerobic and aerobic treatment processes such as sewage, human waste, and wastewater, calcium is added to raw water. There is a method of removing ions by adding ions to generate an insoluble calcium phosphate at a pH of alkaline and separating it. As a calcium ion source used in this method, there are calcium hydroxide (Ca (OH) 2 ), calcium chloride (CaCl 2 ), etc. Among them, when Ca (OH) 2 is used,
An alkaline agent for adjusting pH can be used also.
When CaCl 2 is used, the pH is adjusted by separately adding an alkali such as sodium hydroxide (NaOH).
In addition, the reaction mode includes a precipitation method in which a calcium compound and an alkali agent are added to the raw water in the reaction tank to cause a reaction, and the insolubilized product is separated in the precipitation tank, and a seed is introduced by introducing the raw water into the crystallization tank. There is a crystallization method in which calcium phosphate is precipitated on the surface of the crystal.

【0003】従来、このような脱リン法において、薬注
制御はpHの測定値に基いて行われており、原水に対し
て、pHが一定となるように薬注制御が行われている。
しかし、pH値に基く薬注制御では、リン濃度やカルシ
ウムイオン濃度が変動する原水に対して、含有されるリ
ンを確実にリン酸カルシウムとして不溶化して除去する
ことができず、処理水のリン濃度が原水のリン濃度に対
応して大きく変動するという欠点がある。
Conventionally, in such a dephosphorization method, chemical injection control is performed based on a measured value of pH, and chemical injection control is performed on raw water so that the pH is constant.
However, in the chemical injection control based on the pH value, the contained phosphorus cannot be reliably insolubilized as calcium phosphate and removed from the raw water in which the phosphorus concentration and the calcium ion concentration fluctuate, and the phosphorus concentration of the treated water is reduced. There is a drawback that it fluctuates greatly depending on the phosphorus concentration of the raw water.

【0004】リン含有水にカルシウムイオンを添加して
脱リン処理するに当たり、原水のリン濃度の変動に対応
して確実に脱リン処理を行う方法として、特開平10−
76278号公報には、反応により得られた反応液の残
留カルシウムイオン濃度を測定し、添加したカルシウム
イオン量と残留カルシウムイオン量とから計算により、
原水の溶解性リン(PO−P)濃度(消費されたカル
シウムイオン量と反応してリン酸カルシウムを生成する
リン量)を算出し、算出された原水のリン濃度からこれ
を処理するために必要なカルシウムイオン量を求め、こ
の結果に基いて薬注を行う方法が記載されている。
[0004] In carrying out the dephosphorization treatment by adding calcium ions to the phosphorus-containing water, Japanese Patent Application Laid-Open No.
No. 76278 discloses that the concentration of residual calcium ions in a reaction solution obtained by the reaction is measured and calculated from the amount of calcium ions added and the amount of residual calcium ions.
The concentration of soluble phosphorus (PO 4 -P) in raw water (the amount of phosphorus that reacts with the amount of consumed calcium ions to produce calcium phosphate) is calculated, and from the calculated phosphorus concentration in raw water, it is necessary to treat this. A method is described in which the amount of calcium ions is determined and a drug is injected based on the result.

【0005】[0005]

【発明が解決しようとする課題】しかし、特開平10−
76278号公報記載の方法では、原水のリン濃度を確
実に把握することはできず、このため、脱リン処理を安
定に行うことができない場合があった。即ち、下水処理
水等のリン含有水中のPO−Pイオンをカルシウムイ
オンと反応させて不溶化する場合、カルシウムイオンは
原水中のM−アルカリや空気中の二酸化炭素との反応で
炭酸カルシウム(CaCO)を析出させるため、添加
したカルシウムイオン量と残留カルシウムイオン量とか
ら、原水中のPO−P濃度を正確に求めることはでき
ない。特に、M−アルカリ度等の水質変動の激しい排水
処理の場合や開放系で運転されている脱リン処理系で
は、PO−Pイオン以外の要因で消費されるカルシウ
ムイオン量が多く、またその変動も激しいことから、添
加したカルシウムイオン量と残留カルシウムイオン量と
の差に基いてPO−Pイオン量を求めることは妥当で
はない。
However, Japanese Patent Application Laid-Open No.
In the method described in Japanese Patent No. 76278, the phosphorus concentration of the raw water cannot be reliably grasped, and therefore, there are cases where the phosphorus removal treatment cannot be performed stably. That is, when PO 4 -P ions in phosphorus-containing water such as sewage treatment water are reacted with calcium ions to insolubilize them, calcium ions are converted into calcium carbonate (CaCO 2) by reaction with M-alkali in raw water or carbon dioxide in air. Since 3 ) is precipitated, the PO 4 —P concentration in the raw water cannot be accurately determined from the amount of added calcium ions and the amount of residual calcium ions. In particular, in the case of wastewater treatment in which the water quality fluctuates greatly, such as M-alkaliness, or in a dephosphorization treatment system operated in an open system, the amount of calcium ions consumed by factors other than PO 4 -P ions is large, and Since the fluctuation is severe, it is not appropriate to determine the PO 4 —P ion amount based on the difference between the added calcium ion amount and the residual calcium ion amount.

【0006】本発明は上記従来の問題点を解決し、正リ
ン酸イオンを含有する原水にカルシウムイオンを添加し
てリン酸カルシウム不溶化物を生成させ、これを分離し
て処理水を得るに当たり、リン濃度やカルシウムイオン
濃度、M−アルカリ度等の水質変動が激しい原水中のリ
ンを確実に除去して、リン濃度の低い高水質の処理水を
安定に得ることができる正リン酸含有水の脱リン方法及
び脱リン装置を提供することを目的とする。
[0006] The present invention solves the above-mentioned conventional problems, and adds calcium ions to raw water containing orthophosphate ions to form calcium phosphate insolubilized products. Dephosphorization of orthophosphoric acid-containing water that can reliably remove the phosphorus in raw water with severe water quality fluctuations such as calcium ion concentration, M-alkalinity, etc., and stably obtain high-quality treated water with low phosphorus concentration It is an object to provide a method and a dephosphorization device.

【0007】[0007]

【課題を解決するための手段】本発明の正リン酸含有水
の脱リン方法は、正リン酸イオンを含有する原水にカル
シウムイオンを添加して生成するリン酸カルシウム不溶
化物と処理水とを分離する正リン酸含有水の脱リン方法
において、処理水のpHとカルシウムイオン濃度を測定
し、それぞれの測定値が所定値となるように、原水にp
H調整剤とカルシウムイオンを添加することを特徴とす
る。
According to the method for dephosphorizing orthophosphoric acid-containing water of the present invention, calcium phosphate is added to raw water containing orthophosphate ions to separate calcium phosphate insolubilized product and treated water. In the method of dephosphorizing the orthophosphoric acid-containing water, the pH and the calcium ion concentration of the treated water are measured, and p-water is added to the raw water so that each measured value becomes a predetermined value.
It is characterized by adding an H regulator and calcium ions.

【0008】本発明の脱リン装置は、正リン酸イオンと
カルシウムイオンを反応させてリン酸カルシウム不溶化
物を生成させる反応槽と、該反応槽に正リン酸イオンを
含有する原水を供給する原水供給手段と、該反応槽にカ
ルシウムイオンを添加するカルシウム添加手段と、該反
応槽にpH調整剤を添加するpH調整剤添加手段と、該
反応槽のリン酸カルシウム不溶化物を含む反応液を汚泥
と処理水とに固液分離する固液分離手段と、該処理水の
pHを測定するpH測定手段と、該処理水のカルシウム
イオン濃度を測定するカルシウム濃度測定手段と、該p
H測定手段の出力信号とカルシウム濃度測定手段の出力
信号が入力され、pHとリン酸カルシウムの溶解度積と
の関係から、処理水の正リン酸濃度の所定値を与えるp
Hとカルシウム濃度を演算し、pH調整剤添加手段及び
カルシウム添加手段へそれぞれpH調整剤の添加量及び
カルシウムイオン添加量を制御する制御信号を出力する
演算制御装置とを備えたことを特徴とする。
[0008] The dephosphorization apparatus of the present invention comprises a reaction tank for reacting orthophosphate ions and calcium ions to produce calcium phosphate insolubilized material, and a raw water supply means for supplying raw water containing orthophosphate ions to the reaction tank. A calcium addition means for adding calcium ions to the reaction tank, a pH adjustment agent addition means for adding a pH adjuster to the reaction tank, and a reaction solution containing calcium phosphate insolubilized product in the reaction tank, sludge and treated water. A solid-liquid separation unit for separating solid-liquid into a mixture, a pH measurement unit for measuring the pH of the treated water, a calcium concentration measurement unit for measuring a calcium ion concentration of the treated water,
The output signal of the H measuring means and the output signal of the calcium concentration measuring means are inputted, and a predetermined value of the concentration of normal phosphoric acid in the treated water is given from the relationship between pH and the solubility product of calcium phosphate.
An arithmetic and control unit for calculating H and calcium concentrations, and outputting a control signal for controlling the amount of the pH adjuster and the amount of calcium ion added to the pH adjuster adding means and the calcium adding means, respectively. .

【0009】即ち、本発明者らは、原水の水質変動に影
響されることなく、原水中のリンを確実に除去する薬注
制御方法について鋭意検討を重ねた結果、原水から析出
するリン酸カルシウムには特有の溶解度積が存在し、処
理水のpHと処理水に残存するイオン濃度とから、得ら
れる処理水の溶解性リン(PO−P)濃度を求めるこ
とが可能であること、従って、処理水のPO−P濃度
をどの程度にするかの目標値を定め、このPO−P濃
度が達成される処理水のpHと残存カルシウムイオン濃
度となるように、薬注制御を行えば、安定かつ確実な脱
リン処理を行えることを見出し、本発明を達成させた。
That is, the present inventors have conducted intensive studies on a chemical injection control method for reliably removing phosphorus in raw water without being affected by fluctuations in the quality of raw water. there are inherent solubility product, it from the ion concentration remaining in the treated water and the pH of the treated water, it is possible to determine the solubility of phosphorus (PO 4 -P) concentration in the treated water obtained, therefore, the processing determined whether the target value to what extent the PO 4 -P concentration of water, so that the pH and the residual calcium ion concentration in the treated water is the PO 4 -P concentration is achieved by performing the dosing control, The present inventors have found that stable and reliable dephosphorization can be performed, and have achieved the present invention.

【0010】例えば、原水にカルシウムイオンとアルカ
リ剤を添加してリン酸カルシウムを析出させる脱リン処
理において、処理水のpH、PO−P濃度及びカルシ
ウムイオン濃度を測定してその関係を調べると、図3
(a)に示すような結果が得られる。この図3(a)の
測定値から、処理水のpHと、処理水のリン酸カルシウ
ム(Ca(PO)の溶解度積(log([Ca
2+[PO 3− ))との関係を求めると、図
3(b)の通りであり、溶解度積の理論値に対して実測
値から計算により求められた溶解度積は、約10倍であ
ることがわかる。即ち、溶解度積の理論値の10倍に対
して、処理水pHと処理水の残存カルシウムイオン濃度
を定めることにより、処理水PO−P濃度を求めるこ
とができる。換言すれば、溶解度積の理論値の10倍に
対して、目標とするPO−P濃度を代入することによ
り、処理水pHと処理水に残留させるカルシウムイオン
濃度を定めることができ、このような処理水pH及びカ
ルシウムイオン濃度となるように薬注制御を行うことに
より、目標PO−P濃度の処理水を安定かつ確実に得
ることが可能となる。
[0010] For example, calcium ion and alkali
Dephosphorization to add calcium chloride to precipitate calcium phosphate
Process water pH, PO4-P concentration and calci
Figure 3 shows the relationship between the measured ion concentration and
The result as shown in FIG. In FIG. 3 (a)
From the measured values, the pH of the treated water and the calcium phosphate
(Ca3(PO4)2) (Log ([Ca
2+]3[PO4 3-] 2)) And figure out
3 (b), measured against the theoretical value of the solubility product
The solubility product calculated from the values is about 10 times.
You can see that That is, 10 times the theoretical value of the solubility product
The pH of the treated water and the concentration of residual calcium ions in the treated water
Stipulates that the treated water PO4-Determine the P concentration
Can be. In other words, 10 times the theoretical value of the solubility product
On the other hand, the target PO4-By substituting the P concentration
PH of treated water and calcium ions remaining in treated water
The concentration can be determined.
Controlling chemical dosing to achieve lucium ion concentration
More target PO4-Stably and reliably obtain treated water with P concentration
It becomes possible.

【0011】[0011]

【発明の実施の形態】以下に本発明の実施の形態を詳細
に説明する。
Embodiments of the present invention will be described below in detail.

【0012】本発明においては、溶解性PO−Pを含
有する原水にカルシウム化合物と必要に応じてアルカリ
剤等のpH調整剤を添加してリン酸カルシウムの不溶化
物を析出させることにより脱リン処理するに当たり、処
理水のpHとカルシウムイオン濃度を測定し、この測定
値が所定の値となるようにカルシウム化合物及びpH調
整剤の添加量を制御する。
In the present invention, a dephosphorization treatment is performed by adding a calcium compound and, if necessary, a pH adjuster such as an alkali agent to raw water containing soluble PO 4 -P to precipitate an insolubilized product of calcium phosphate. In this case, the pH of the treated water and the calcium ion concentration are measured, and the amounts of the calcium compound and the pH adjuster are controlled so that the measured values become predetermined values.

【0013】即ち、前述の如く、このような脱リン処理
に当たり、実測値から求められた処理水のリン酸カルシ
ウムの溶解度積は、処理水pHに対して所定の値とな
り、この溶解度積は、理論値の約10倍である。従っ
て、測定されたpH値に対応する溶解度積(この値は理
論値の約10倍となる)に、目標とするPO−P濃度
を代入することにより、このPO−P濃度を得るため
の処理水のカルシウムイオン濃度を算出することができ
るので、処理水のカルシウムイオン濃度が算出されたカ
ルシウムイオン濃度となるように、カルシウム化合物の
添加量を制御すれば良い。
That is, as described above, in such a dephosphorization treatment, the solubility product of calcium phosphate in the treated water obtained from the actually measured value is a predetermined value with respect to the pH of the treated water, and the solubility product is a theoretical value. About 10 times. Therefore, by substituting the target PO 4 -P concentration into the solubility product corresponding to the measured pH value (this value is about 10 times the theoretical value), the PO 4 -P concentration can be obtained. Since the calcium ion concentration of the treated water can be calculated, the amount of the calcium compound added may be controlled so that the calcium ion concentration of the treated water becomes the calculated calcium ion concentration.

【0014】本発明の好適な実施形態としては、処理水
のpH測定手段の測定値に基いて、処理水のpHが一定
となるようにアルカリ剤等のpH調整剤の添加量を制御
すると共に、このpH値に対応する溶解度積から、目標
とする処理水PO−P濃度を得るためのカルシウムイ
オン濃度を算出し、カルシウムイオン濃度測定手段の測
定値がこのカルシウムイオン濃度となるように、カルシ
ウム化合物の添加量を制御する方法が挙げられる。
According to a preferred embodiment of the present invention, the amount of a pH adjuster such as an alkali agent is controlled so that the pH of the treated water is constant, based on the value measured by the pH measuring means of the treated water. From the solubility product corresponding to this pH value, a calcium ion concentration for obtaining the target treated water PO 4 -P concentration is calculated, and the measured value of the calcium ion concentration measuring means is the calcium ion concentration. A method of controlling the amount of the calcium compound to be added is exemplified.

【0015】なお、本発明では、このように、pHとカ
ルシウムイオン濃度とを個別に制御することから、カル
シウム化合物としては、アルカリ性のCa(OH)
用いるよりも、中性のCaClを用い、pH調整のた
めにNaOH等のアルカリ剤を添加することが好まし
い。
In the present invention, since the pH and the calcium ion concentration are individually controlled as described above, neutral CaCl 2 is used as the calcium compound rather than using alkaline Ca (OH) 2. Preferably, an alkali agent such as NaOH is added for pH adjustment.

【0016】このような本発明の正リン酸含有水の脱リ
ン方法及び脱リン装置で処理する原水としては、下水処
理水、下水汚泥集約処理で発生する排水が挙げられ、本
発明は、このような原水を反応槽でカルシウム化合物と
必要に応じてアルカリ剤を添加して反応させ、不溶化物
を沈殿槽で分離する沈殿法に対しても、原水を晶折槽に
導入して種晶の表面にリン酸カルシウムを析出させる晶
折法に対しても有効に適用可能である。
The raw water to be treated by the method for dephosphorizing orthophosphoric acid-containing water and the dephosphorization apparatus of the present invention includes sewage treated water and wastewater generated by sewage sludge intensive treatment. For the precipitation method in which such raw water is reacted by adding a calcium compound and an alkali agent as necessary in a reaction tank, and the insolubilized substance is separated in a precipitation tank, the raw water is introduced into a crystallizing tank to form seed crystals. The present invention can be effectively applied to a crystallization method in which calcium phosphate is precipitated on the surface.

【0017】[0017]

【実施例】以下に実施例及び比較例を挙げて本発明をよ
り具体的に説明する。
The present invention will be described more specifically below with reference to examples and comparative examples.

【0018】実施例1 図1に示す装置により合成排水の処理を行った。Example 1 A synthetic wastewater was treated by the apparatus shown in FIG.

【0019】まず、合成排水(PO−P:10mg/
L,Ca:39mg/L,M−アルカリ:88mg/
L)を原水槽1に導入し、この原水槽1において、正リ
ン酸塩(リン酸二水素一ナトリウム:NaHPO
水溶液を添加し、このときの注入ポンプPの稼動時間
や回転数を変えることにより、原水のPO−P濃度を
10〜50mg/Lの範囲で変動させた。
[0019] First of all, synthetic drainage (PO 4 -P: 10mg /
L, Ca: 39 mg / L, M-alkali: 88 mg /
L) is introduced into the raw water tank 1, where the orthophosphate (monosodium dihydrogen phosphate: NaH 2 PO 4 ) is introduced.
Adding an aqueous solution, by varying the operating time and rotational speed of the infusion pump P 1 at this time, the PO 4 -P concentration of the raw water was varied in the range of 10 to 50 mg / L.

【0020】この合成排水にCaCl水溶液を注入し
た後、攪拌装置を備える第1反応槽2及び第3反応槽3
に順次送給して反応させた後、沈殿槽4で固液分離し
た。なお、第1反応槽2では、アルカリ剤としてNaO
H水溶液を添加してpH調整した。沈殿槽4の分離汚泥
は、一部を第1反応槽2に返送し、残部を系外へ排出し
た。また、分離液は処理水槽5を経て系外へ取り出し
た。
After injecting the aqueous solution of CaCl 2 into the synthetic waste water, the first reaction tank 2 and the third reaction tank 3 having a stirring device are provided.
After that, the mixture was sequentially fed to the reaction vessel and reacted, and then subjected to solid-liquid separation in the precipitation tank 4. In the first reaction tank 2, NaO was used as an alkaline agent.
An aqueous H solution was added to adjust the pH. A part of the separated sludge in the settling tank 4 was returned to the first reaction tank 2, and the remaining part was discharged out of the system. The separated liquid was taken out of the system via the treatment water tank 5.

【0021】本実施例では、この処理水槽5にpH計6
とCaイオンセンサ7を設け、pH計6の測定値が9.
0となるように、NaOH水溶液の注入ポンプPの稼
動を制御すると共に、Caイオンセンサ7の測定値が3
5〜40mg/LとなるようにCaCl水溶液注入ポ
ンプPの稼動を制御した。
In the present embodiment, a pH meter 6
And a Ca ion sensor 7, and the measured value of the pH meter 6 is 9.
As becomes 0 and controls the operation of the infusion pump P 3 of NaOH solution, the measured value of Ca ion sensor 7 3
Was controlled operation of CaCl 2 aqueous infusion pump P 2 so that 5 to 40 mg / L.

【0022】このとき、CaCl水溶液の添加量は2
5〜95mg−Ca2+/Lの範囲で変動した。
At this time, the addition amount of the CaCl 2 aqueous solution is 2
It varied in the range of 5-95 mg-Ca2 + / L.

【0023】原水のPO−P濃度と処理水のPO
P濃度の経時変化は図2に示す通りであり、原水のPO
−P濃度の変動にも係わらず、処理水のPO−P濃
度を約5mg/L程度に安定に維持することができた。
[0023] of the PO 4 -P concentration of the raw water and treated water PO 4 -
The time course of the P concentration is as shown in FIG.
Despite the fluctuation of the 4- P concentration, the PO 4 -P concentration of the treated water could be stably maintained at about 5 mg / L.

【0024】比較例1 実施例1において、Caイオンセンサを設けず、pH計
による制御のみで、CaCl水溶液の添加は、50〜
55mg−Ca2+/Lで一定としたこと以外は実施例
1と同様にして処理を行った。その結果、原水のPO
−P濃度変動に応じて処理水のPO−P濃度は、図2
に示す如く大きく変動し、安定な処理を行うことはでき
なかった。
[0024] In Comparative Example 1 Example 1, without providing the Ca ion sensor, only the control by the pH meter, the addition of CaCl 2 aqueous solution, 50
The treatment was carried out in the same manner as in Example 1 except that it was kept constant at 55 mg-Ca 2+ / L. As a result, PO 4 of raw water
The PO 4 -P concentration of the treated water is shown in FIG.
As shown in the figure, it fluctuated greatly, and stable processing could not be performed.

【0025】[0025]

【発明の効果】以上詳述した通り、本発明の正リン酸含
有水の脱リン方法及び脱リン装置によれば、正リン酸イ
オンを含有する原水にカルシウムイオンを添加してリン
酸カルシウム不溶化物を生成させ、これを分離して処理
水を得るに当たり、リン濃度やカルシウムイオン濃度、
M−アルカリ度等の水質変動が激しい原水中のリンを確
実に除去して、リン濃度の低い高水質の処理水を安定に
得ることができる。
As described above in detail, according to the method and apparatus for dephosphorizing orthophosphoric acid-containing water of the present invention, calcium phosphate is added to raw water containing orthophosphate ions to remove calcium phosphate insolubilized product. In producing and separating water to obtain treated water, phosphorus concentration, calcium ion concentration,
It is possible to reliably remove the phosphorus in the raw water whose water quality fluctuates greatly, such as M-alkalinity, and stably obtain high-quality treated water having a low phosphorus concentration.

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

【図1】実施例1で用いた脱リン装置を示す系統図であ
る。
FIG. 1 is a system diagram showing a dephosphorization device used in Example 1.

【図2】実施例1及び比較例1の結果を示すグラフであ
る。
FIG. 2 is a graph showing the results of Example 1 and Comparative Example 1.

【図3】(a)図は、処理水のpHとカルシウムイオン
濃度及びPO−P濃度との関係を示すグラフであり、
(b)図は、処理水のpHと溶解度積との関係を示すグ
ラフである。
FIG. 3 (a) is a graph showing the relationship between the pH of treated water and the calcium ion concentration and PO 4 -P concentration,
(B) is a graph showing the relationship between the pH of the treated water and the solubility product.

【符号の説明】[Explanation of symbols]

1 原水槽 2 第1反応槽 3 第2反応槽 4 沈殿槽 5 処理水槽 6 pH計 7 Caイオンセンサ DESCRIPTION OF SYMBOLS 1 Raw water tank 2 1st reaction tank 3 2nd reaction tank 4 Sedimentation tank 5 Treatment water tank 6 pH meter 7 Ca ion sensor

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 正リン酸イオンを含有する原水にカルシ
ウムイオンを添加して生成するリン酸カルシウム不溶化
物と処理水とを分離する正リン酸含有水の脱リン方法に
おいて、 処理水のpHとカルシウムイオン濃度を測定し、それぞ
れの測定値が所定値となるように、原水にpH調整剤と
カルシウムイオンを添加することを特徴とする正リン酸
含有水の脱リン方法。
1. A method for dephosphorizing orthophosphoric acid-containing water, wherein calcium phosphate is added to raw water containing orthophosphate ions to separate calcium phosphate insolubilized water and treated water, wherein the pH of the treated water and the calcium ion A method for dephosphorizing orthophosphoric acid-containing water, comprising measuring a concentration and adding a pH adjuster and calcium ions to the raw water so that each measured value becomes a predetermined value.
【請求項2】 正リン酸イオンとカルシウムイオンを反
応させてリン酸カルシウム不溶化物を生成させる反応槽
と、 該反応槽に正リン酸イオンを含有する原水を供給する原
水供給手段と、 該反応槽にカルシウムイオンを添加するカルシウム添加
手段と、 該反応槽にpH調整剤を添加するpH調整剤添加手段
と、 該反応槽のリン酸カルシウム不溶化物を含む反応液を汚
泥と処理水とに固液分離する固液分離手段と、 該処理水のpHを測定するpH測定手段と、 該処理水のカルシウムイオン濃度を測定するカルシウム
濃度測定手段と、 該pH測定手段の出力信号とカルシウム濃度測定手段の
出力信号が入力され、pHとリン酸カルシウムの溶解度
積との関係から、処理水の正リン酸濃度の所定値を与え
るpHとカルシウム濃度を演算し、pH調整剤添加手段
及びカルシウム添加手段へそれぞれpH調整剤の添加量
及びカルシウムイオン添加量を制御する制御信号を出力
する演算制御装置とを備えたことを特徴とする脱リン装
置。
2. A reaction tank for reacting orthophosphate ions with calcium ions to produce calcium phosphate insolubilized material, raw water supply means for supplying raw water containing orthophosphate ions to the reaction tank, Calcium addition means for adding calcium ions, pH adjustment agent addition means for adding a pH adjuster to the reaction tank, solid-liquid separation of the reaction solution containing the calcium phosphate insolubilized substance of the reaction tank into sludge and treated water. Liquid separating means; pH measuring means for measuring the pH of the treated water; calcium concentration measuring means for measuring the calcium ion concentration of the treated water; and an output signal of the pH measuring means and an output signal of the calcium concentration measuring means. From the relationship between the pH and the solubility product of calcium phosphate, the pH and calcium concentration that give a predetermined value of the orthophosphoric acid concentration of the treated water are calculated, Dephosphorization device being characterized in that an arithmetic control unit for outputting a control signal for controlling the amount of calcium ions added amount of each pH adjusting agent to Seizai adding means and calcium addition means.
JP2001003854A 2001-01-11 2001-01-11 Method and apparatus for dephosphorization of water containing orthophosphoric acid Expired - Fee Related JP4631169B2 (en)

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Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58223479A (en) * 1982-06-21 1983-12-26 Kurita Water Ind Ltd Device for treating water containing phosphate
JPS60202788A (en) * 1984-03-22 1985-10-14 Kurita Water Ind Ltd Treating apparatus for waste water containing fluorine and phosphorus
JPS60225692A (en) * 1984-04-23 1985-11-09 Hitachi Plant Eng & Constr Co Ltd Method and apparatus for controlling contact crystallization phosphorization process
JPS61153191A (en) * 1984-12-26 1986-07-11 Ebara Infilco Co Ltd Catalytic dephosphorizer
JPS62250990A (en) * 1986-04-25 1987-10-31 Ataka Kogyo Kk Treatment of waste water containing phosphate ion
JPH091154A (en) * 1995-06-16 1997-01-07 Kurita Water Ind Ltd Treatment of phosphoric acid-containing waste water
JPH1076278A (en) * 1996-09-03 1998-03-24 Unitika Ltd Apparatus for controlling addition of phosphorus removing agent
JPH1085761A (en) * 1996-09-13 1998-04-07 Japan Organo Co Ltd Method and apparatus for treating drainage containing fluorine
JPH10128344A (en) * 1996-11-06 1998-05-19 Japan Organo Co Ltd Apparatus and method for treating fluorine-containing drainage

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58223479A (en) * 1982-06-21 1983-12-26 Kurita Water Ind Ltd Device for treating water containing phosphate
JPS60202788A (en) * 1984-03-22 1985-10-14 Kurita Water Ind Ltd Treating apparatus for waste water containing fluorine and phosphorus
JPS60225692A (en) * 1984-04-23 1985-11-09 Hitachi Plant Eng & Constr Co Ltd Method and apparatus for controlling contact crystallization phosphorization process
JPS61153191A (en) * 1984-12-26 1986-07-11 Ebara Infilco Co Ltd Catalytic dephosphorizer
JPS62250990A (en) * 1986-04-25 1987-10-31 Ataka Kogyo Kk Treatment of waste water containing phosphate ion
JPH091154A (en) * 1995-06-16 1997-01-07 Kurita Water Ind Ltd Treatment of phosphoric acid-containing waste water
JPH1076278A (en) * 1996-09-03 1998-03-24 Unitika Ltd Apparatus for controlling addition of phosphorus removing agent
JPH1085761A (en) * 1996-09-13 1998-04-07 Japan Organo Co Ltd Method and apparatus for treating drainage containing fluorine
JPH10128344A (en) * 1996-11-06 1998-05-19 Japan Organo Co Ltd Apparatus and method for treating fluorine-containing drainage

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