JP2001314874A - Apparatus and method for treating phosphorus- containing water - Google Patents

Apparatus and method for treating phosphorus- containing water

Info

Publication number
JP2001314874A
JP2001314874A JP2000136786A JP2000136786A JP2001314874A JP 2001314874 A JP2001314874 A JP 2001314874A JP 2000136786 A JP2000136786 A JP 2000136786A JP 2000136786 A JP2000136786 A JP 2000136786A JP 2001314874 A JP2001314874 A JP 2001314874A
Authority
JP
Japan
Prior art keywords
mixing tank
water
phosphorus
seed crystal
calcium
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
JP2000136786A
Other languages
Japanese (ja)
Inventor
Ichiro Sumita
一郎 住田
Tetsuro Fukase
哲朗 深瀬
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
Original Assignee
Kurita Water Industries Ltd
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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP2000136786A priority Critical patent/JP2001314874A/en
Publication of JP2001314874A publication Critical patent/JP2001314874A/en
Pending legal-status Critical Current

Links

Landscapes

  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To prevent the outflow of fine calcium phosphate particles from a calcium phosphate crystallization reaction column and the formation of scale in the column, in an apparatus and method for treating phosphorus-containing water by removing and recovering phosphate groups in phosphorus-containing water as calcium phosphate. SOLUTION: In the phosphorus-containing water treatment apparatus equipped with a mixing tank for mixing phosphate group-containing water, a water soluble calcium compound and a pH controller and a crystallization reaction column having the introducing port of the outflow liquid of the mixing tank disposed at the lower part thereof and having a treated water outflow port disposed at the upper part thereof and housing seed crystals, a seed crystal return means for returning seed crystals in the crystallization reaction column to the mixing tank is provided. In the phosphorus-containing water treatment method, phosphate group-containing water, the water soluble calcium compound and the pH controller are mixed in the presence of seed crystals in the mixing tank to be introduced into the lower part of the crystallization reaction column and treated water is allowed to flow out of the upper part of the reaction column and the seed crystals in the crystallization reaction column are returned to the mixing tank.

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、リン含有水の処理
装置及び処理方法に関する。さらに詳しくは、本発明
は、リン含有水中のリン酸根をリン酸カルシウムとして
除去、回収するリン含有水の処理装置及び処理方法にお
いて、リン酸カルシウム晶析反応塔からの微細なリン酸
カルシウム粒子の流出及び塔内でのスケール生成を防止
することができるリン含有水の処理装置及び処理方法に
関する。
[0001] The present invention relates to an apparatus and a method for treating phosphorus-containing water. More specifically, the present invention relates to a treatment apparatus and a treatment method for removing and recovering phosphate groups in phosphorus-containing water as calcium phosphate, wherein the fine calcium phosphate particles flow out from the calcium phosphate crystallization reaction tower and the inside thereof. The present invention relates to a phosphorus-containing water treatment device and treatment method capable of preventing scale formation.

【0002】[0002]

【従来の技術】下水、排水などのリン含有水から、リン
を除去する脱リン方法として、凝集沈殿法、吸着法、晶
析法などが挙げられる。鉄塩、アルミニウム塩を用いる
凝集沈殿法では、大量の汚泥が生成する。カルシウム塩
による凝集では、多量のカルシウム塩が必要であり、さ
らにpHを強アルカリ性にするために、スケールが生成し
やすく、処理水の中和が必要である。また、吸着法で
は、吸着材によって吸着量に限界があり、吸着が飽和し
た時点で吸着材の交換又は再生が必要となる。これに対
して、晶析法では、半永久的に連続運転が可能であり、
汚泥発生量も抑えられるという特長がある。リン含有排
水から、リンを1mgP/L以下まで除去する晶析法とし
て、リン酸カルシウム晶析法がある。この方法は、カル
シウムイオンの存在下で、かつpH6以上の条件下に、リ
ン酸カルシウムを含む種晶と接触させることにより、液
中のリンをリン酸カルシウムとして析出させ除去するも
のである。このときに起こる反応は、反応条件によって
異なるが、通常は次式で表される。 5Ca2+ + 3HPO4 2- + 4OH- → Ca5(PO4)3OH + 3H2O …[1] 水中に存在させるカルシウムイオンや水酸イオンの量は
反応当量よりも過剰とするが、あまり多量に存在する
と、種晶以外の場所で微細な沈殿が析出したり、また、
炭酸カルシウムなどの不純物が生成する場合がある。し
たがって、微細な粒子の発生を抑え、種晶の表面にのみ
リン酸カルシウムが析出するように、被処理水にカルシ
ウム塩やアルカリ剤を添加する必要がある。被処理水と
カルシウム塩やアルカリ剤を混和してから、反応塔内で
種晶と接触させる方式では、反応塔に流入する前段階で
は微細な粒子が発生しない条件に抑える必要がある。こ
の方式では、反応塔流入部でのカルシウムイオン濃度、
pH条件が制限され、処理水の水質や、反応塔の容量制限
の要求を満足できない場合がある。反応装置の小型化す
なわち反応の高速化を図るためには、カルシウムイオン
濃度とpHの少なくともいずれか一方を上げる必要がある
が、上記のように制限がある。種晶が存在する状態でカ
ルシウム塩とアルカリ剤を添加すると、種晶がない状態
に比べて、種晶表面以外での微細な粒子の発生を抑制す
ることができるが、反応塔内で種晶と接触する直前、又
は、種晶層内で薬剤を添加すると、密度流発生の危険性
があり薬剤の拡散をうまく制御することができない。ま
た、種晶層内での薬剤の拡散を優先すると、反応塔内が
完全混合状態に近づき、処理効率が低下したり、あるい
は、別途に種晶と処理水の分離手段が必要となるなどの
問題があった。
2. Description of the Related Art As a method for removing phosphorus from phosphorus-containing water such as sewage and wastewater, there are a coagulation sedimentation method, an adsorption method, and a crystallization method. In the coagulation sedimentation method using an iron salt or an aluminum salt, a large amount of sludge is generated. Coagulation by calcium salts requires a large amount of calcium salts, and furthermore, scales are easily formed in order to make the pH strongly alkaline, and neutralization of treated water is required. In addition, in the adsorption method, the amount of adsorption is limited by the adsorbent, and it is necessary to replace or regenerate the adsorbent when the adsorption is saturated. In contrast, the crystallization method enables semi-permanent continuous operation,
The feature is that the amount of generated sludge can be reduced. As a crystallization method for removing phosphorus from a phosphorus-containing wastewater to 1 mg P / L or less, there is a calcium phosphate crystallization method. In this method, phosphorus in a liquid is precipitated and removed as calcium phosphate by bringing it into contact with a seed crystal containing calcium phosphate in the presence of calcium ions and at a pH of 6 or more. The reaction that takes place at this time depends on the reaction conditions, but is usually represented by the following formula. 5Ca 2+ + 3HPO 4 2- + 4OH → Ca 5 (PO 4 ) 3 OH + 3H 2 O [1] The amount of calcium ions and hydroxyl ions present in water is set to be larger than the reaction equivalent. If present in a large amount, fine precipitates will be deposited in places other than the seed crystal,
Impurities such as calcium carbonate may be generated. Therefore, it is necessary to add a calcium salt or an alkali agent to the water to be treated so as to suppress generation of fine particles and to precipitate calcium phosphate only on the surface of the seed crystal. In a method in which the water to be treated is mixed with a calcium salt or an alkaline agent and then brought into contact with a seed crystal in the reaction tower, it is necessary to suppress the conditions such that fine particles are not generated before flowing into the reaction tower. In this method, the calcium ion concentration at the inlet of the reaction tower,
In some cases, the pH conditions are limited, and the quality of the treated water and the requirement for limiting the volume of the reaction tower cannot be satisfied. In order to reduce the size of the reaction apparatus, that is, to speed up the reaction, it is necessary to increase at least one of the calcium ion concentration and the pH, but there are limitations as described above. When a calcium salt and an alkali agent are added in the presence of a seed crystal, the generation of fine particles other than the surface of the seed crystal can be suppressed as compared with a state without the seed crystal. If the drug is added immediately before contacting with or within the seed crystal layer, there is a risk of generating a density flow, and the diffusion of the drug cannot be controlled well. In addition, if priority is given to the diffusion of the drug in the seed crystal layer, the inside of the reaction tower approaches a completely mixed state, and the treatment efficiency is reduced, or a separate means for separating the seed crystal and the treated water is required. There was a problem.

【0003】[0003]

【発明が解決しようとする課題】本発明は、リン含有水
中のリン酸根をリン酸カルシウムとして除去、回収する
リン含有水の処理装置及び処理方法において、リン酸カ
ルシウム晶析反応塔からの微細なリン酸カルシウム粒子
の流出及び塔内でのスケール生成を防止することができ
るリン含有水の処理装置及び処理方法を提供することを
目的としてなされたものである。
DISCLOSURE OF THE INVENTION The present invention relates to an apparatus and a method for treating phosphorus-containing water for removing and recovering phosphate groups from the phosphorus-containing water as calcium phosphate. Another object of the present invention is to provide an apparatus and method for treating phosphorus-containing water that can prevent scale formation in a tower.

【0004】[0004]

【課題を解決するための手段】本発明者らは、上記の課
題を解決すべく鋭意研究を重ねた結果、リン含有水と水
溶性カルシウム化合物とpH調整剤との混和槽に晶析反応
塔の種晶を返送し、種晶の存在下に混和を行うことによ
り、リン酸カルシウム晶析反応塔からの微細な粒子の流
出や、不純物の生成を抑え、より効率的な脱リンが可能
となることを見いだし、この知見に基づいて本発明を完
成するに至った。すなわち、本発明は、(1)リン酸根
を含有する水と水溶性カルシウム化合物とpH調整剤との
混和槽と、該混和槽の流出液の導入口を塔下部に有し、
処理水の流出口を塔上部に有し、かつ種晶を内蔵する晶
析反応塔とを備えたリン含有水の処理装置において、前
記晶析反応塔内の種晶を前記混和槽に返送する種晶返送
手段を有することを特徴とするリン含有水の処理装置、
(2)リン酸根を含有する水に水溶性カルシウム化合物
とpH調整剤を添加し、リン化合物を晶析させて除去する
リン含有水の処理方法において、リン酸根を含有する水
と水溶性カルシウム化合物とpH調整剤とを、種晶の存在
下に混和槽において混和したのち、種晶を内蔵する晶析
反応塔下部に導入し、リン化合物を晶析させつつ晶析反
応塔内に通水し、処理水を反応塔上部より流出させると
ともに、晶析反応塔内の種晶を混和槽に返送することを
特徴とするリン含有水の処理方法、及び、(3)混和槽
内の種晶濃度が1〜30重量%になるように、晶析反応
塔内の種晶を混和槽に返送する第2項記載のリン含有水
の処理方法、を提供するものである。さらに、本発明の
好ましい態様として、(4)水溶性カルシウム化合物
を、リンに対してカルシウムが2〜20モル倍になるよ
うに添加する第2項記載のリン含有水の処理方法、
(5)混和槽の流出液のpHが7〜12となるように、pH
調整剤を添加する第2項記載のリン含有水の処理方法、
及び、(6)種晶の平均粒径が、0.05〜1mmである
第2項記載のリン含有水の処理方法、を挙げることがで
きる。
Means for Solving the Problems The inventors of the present invention have conducted intensive studies to solve the above-mentioned problems, and as a result, the crystallization reaction tower was added to a mixing tank of phosphorus-containing water, a water-soluble calcium compound and a pH adjuster. By returning the seed crystal and mixing in the presence of the seed crystal, the outflow of fine particles from the calcium phosphate crystallization reaction tower and the generation of impurities can be suppressed, and more efficient dephosphorization becomes possible. And completed the present invention on the basis of this finding. That is, the present invention has (1) a mixing tank of water containing a phosphate group, a water-soluble calcium compound and a pH adjuster, and an inlet for an effluent of the mixing tank at the bottom of the tower;
In a treatment device for phosphorus-containing water having an outlet for treated water at the top of the tower and a crystallization reaction tower containing a seed crystal, the seed crystal in the crystallization reaction tower is returned to the mixing tank. An apparatus for treating phosphorus-containing water, comprising a seed crystal returning means,
(2) A method for treating a phosphorus-containing water in which a water-soluble calcium compound and a pH adjuster are added to water containing a phosphate group, and the phosphorus compound is crystallized and removed. And the pH adjuster are mixed in a mixing tank in the presence of the seed crystal, and then introduced into the lower portion of the crystallization reaction tower containing the seed crystal, and water is passed through the crystallization reaction tower while crystallizing the phosphorus compound. And (3) a seed crystal concentration in the mixing tank, wherein the treated water is discharged from the upper part of the reaction tower, and a seed crystal in the crystallization reaction tower is returned to the mixing tank. 3. The method for treating phosphorus-containing water according to claim 2, wherein the seed crystals in the crystallization reaction tower are returned to the mixing tank so that the content of the phosphorus is 1 to 30% by weight. Further, as a preferred embodiment of the present invention, the method for treating phosphorus-containing water according to claim 2, wherein (4) the water-soluble calcium compound is added so that calcium is added in an amount of 2 to 20 times by mole of phosphorus.
(5) Adjust the pH so that the effluent of the mixing tank has a pH of 7 to 12.
3. The method for treating phosphorus-containing water according to claim 2, wherein a regulator is added.
And (6) the method for treating phosphorus-containing water according to item 2, wherein the seed crystal has an average particle size of 0.05 to 1 mm.

【0005】[0005]

【発明の実施の形態】本発明のリン含有水の処理装置
は、リン酸根を含有する水と水溶性カルシウム化合物と
pH調整剤との混和槽と、該混和槽の流出液の導入口を塔
下部に有し、処理水の流出口を塔上部に有し、かつ種晶
を内蔵する晶析反応塔とを備えたリン含有水の処理装置
において、前記晶析反応塔内の種晶を前記混和槽に返送
する種晶返送手段を有する。本発明のリン含有水の処理
方法は、リン酸根を含有する水に水溶性カルシウム化合
物とpH調整剤を添加し、リン化合物を晶析させて除去す
るリン含有水の処理方法において、リン酸根を含有する
水と水溶性カルシウム化合物とpH調整剤とを、種晶の存
在下に混和槽において混和したのち、種晶を内蔵する晶
析反応塔下部に導入し、リン化合物を晶析させつつ晶析
反応塔内に通水し、処理水を反応塔上部より流出させる
とともに、晶析反応塔内の種晶を混和槽に返送する。図
1は、本発明装置の一態様の工程系統図である。混和槽
1には、原水が送り込まれるとともに、晶析反応塔2内
に形成された種晶充填層3から、種晶返送配管4を通じ
て種晶が返送される。混和槽には、さらに水溶性カルシ
ウム化合物とpH調整剤が添加され、撹拌により均一に混
合される。pH調整剤の添加量は、図1に示すように混和
槽にpH計を設けて制御することができ、あるいは、反応
塔入口にpH計を設けて制御することもできる。混和槽の
流出液は、流出液配管5を通じて反応塔下部の流出液導
入口に導かれる。反応塔内には、種晶充填層3が形成さ
れていて、リン酸カルシウムが過飽和の状態となった混
和槽の流出液は、種晶の表面にリン酸カルシウムを晶析
しつつ塔内を上向流で流れ、リン濃度の低い処理水とな
って、塔上部に設けられた流出口より流出する。
BEST MODE FOR CARRYING OUT THE INVENTION The apparatus for treating phosphorus-containing water according to the present invention comprises water containing a phosphate group and a water-soluble calcium compound.
A mixing tank with a pH adjuster, a crystallization reaction tower having an inlet for the effluent of the mixing tank at the bottom of the tower, an outlet for treated water at the top of the tower, and containing a seed crystal. The apparatus for treating phosphorus-containing water has a seed crystal returning means for returning seed crystals in the crystallization reaction tower to the mixing tank. In the method for treating phosphorus-containing water of the present invention, the method for treating a phosphorus-containing water comprises adding a water-soluble calcium compound and a pH adjuster to water containing a phosphate group, and crystallizing and removing the phosphorus compound. The water, the water-soluble calcium compound and the pH adjuster are mixed in a mixing tank in the presence of seed crystals, and then introduced into the lower portion of the crystallization reaction tower containing the seed crystals, and the phosphorus compound is crystallized while crystallizing. Water is passed through the precipitation reaction tower, and the treated water is allowed to flow out of the upper part of the reaction tower, and the seed crystals in the crystallization reaction tower are returned to the mixing tank. FIG. 1 is a process flow diagram of one embodiment of the apparatus of the present invention. Raw water is fed into the mixing tank 1, and seed crystals are returned from the seed crystal packed bed 3 formed in the crystallization reaction tower 2 through the seed crystal return pipe 4. A water-soluble calcium compound and a pH adjuster are further added to the mixing tank, and are uniformly mixed by stirring. As shown in FIG. 1, the addition amount of the pH adjuster can be controlled by providing a pH meter in the mixing tank, or by providing a pH meter at the inlet of the reaction tower. The effluent from the mixing tank is led to the effluent inlet at the bottom of the reaction tower through the effluent pipe 5. In the reaction tower, a seed crystal packed bed 3 is formed, and the effluent of the mixing tank in which calcium phosphate is in a supersaturated state flows upward in the tower while crystallizing calcium phosphate on the surface of the seed crystal. It flows into treated water having a low phosphorus concentration and flows out from an outlet provided at the top of the tower.

【0006】本発明方法に用いる水溶性カルシウム化合
物に特に制限はなく、例えば、塩化カルシウム、臭化カ
ルシウム、ヨウ化カルシウム、亜硝酸カルシウム、硝酸
カルシウム、硫酸カルシウム、塩素酸カルシウム、次亜
塩素酸カルシウム、ホスフィン酸カルシウムなどの無機
カルシウム塩、ギ酸カルシウム、酢酸カルシウム、プロ
ピオン酸カルシウム、アセチルサルチル酸カルシウム、
フェノールスルホン酸カルシウムなどの有機カルシウム
塩や、水酸化カルシウムなどを挙げることができる。本
発明方法において、水溶性カルシウム化合物の添加量に
特に制限はないが、リンに対してカルシウムが2〜20
モル倍であることが好ましく、5〜15倍であることが
より好ましい。すなわち、上記の化学反応式[1]で示
される理論量の1.2〜12倍の水溶性カルシウム化合
物を添加することが好ましく、3〜9倍の水溶性カルシ
ウム化合物を添加することがより好ましい。リンに対す
るカルシウムの比が2モル倍未満であると、処理水のリ
ン濃度が十分に低下しないおそれがある。リンに対する
カルシウムの比が20モル倍を超えると、過剰のカルシ
ウムのために処理水の水質が低下するおそれがある。本
発明方法に用いるpH調整剤に特に制限はなく、例えば、
水酸化ナトリウム、水酸化カリウム、炭酸ナトリウム、
炭酸カリウム、アンモニアなどを挙げることができる。
また、水溶性カルシウム化合物として水酸化カルシウム
を用いた場合は、水酸化カルシウムにpH調整剤を兼ねさ
せることができる。pH調整剤は、混和槽の流出液のpHが
7〜12となるように添加することが好ましく、pHが9
〜10となるように添加することがより好ましい。混和
槽の流出液のpHは、混和槽から晶析反応塔の入口までの
間の任意の箇所において測定することができる。混和槽
の流出液のpH測定値に基づいて、pH調整剤の添加量を制
御することができる。
The water-soluble calcium compound used in the method of the present invention is not particularly limited. Examples thereof include calcium chloride, calcium bromide, calcium iodide, calcium nitrite, calcium nitrate, calcium sulfate, calcium chlorate, and calcium hypochlorite. , Inorganic calcium salts such as calcium phosphinate, calcium formate, calcium acetate, calcium propionate, calcium acetylsalicylate,
Organic calcium salts such as calcium phenolsulfonate and calcium hydroxide can be mentioned. In the method of the present invention, the amount of the water-soluble calcium compound to be added is not particularly limited.
It is preferably a molar ratio, more preferably 5 to 15 times. That is, it is preferable to add 1.2 to 12 times the water-soluble calcium compound, and more preferably 3 to 9 times the water-soluble calcium compound, of the theoretical amount represented by the chemical reaction formula [1]. . If the ratio of calcium to phosphorus is less than 2 molar times, the phosphorus concentration of the treated water may not be sufficiently reduced. If the ratio of calcium to phosphorus exceeds 20 mol times, the quality of treated water may be reduced due to excessive calcium. There is no particular limitation on the pH adjuster used in the method of the present invention, for example,
Sodium hydroxide, potassium hydroxide, sodium carbonate,
Potassium carbonate, ammonia and the like can be mentioned.
When calcium hydroxide is used as the water-soluble calcium compound, calcium hydroxide can also serve as a pH adjuster. The pH adjuster is preferably added so that the effluent of the mixing tank has a pH of 7 to 12,
More preferably, it is added so as to be from 10 to 10. The pH of the effluent of the mixing tank can be measured at any point between the mixing tank and the inlet of the crystallization reaction tower. The addition amount of the pH adjuster can be controlled based on the measured value of the pH of the effluent of the mixing tank.

【0007】本発明装置は、晶析反応塔内に種晶を内蔵
する。種晶として用いる物質は、リン含有水中のリン酸
根と添加した水溶性カルシウム化合物の反応により生成
する物質又はそれと類似の物質であり、例えば、ヒドロ
キシアパタイト、フルオロアパタイト、クロロアパタイ
トなどのリン灰石や、リン酸三石灰などのリン酸カルシ
ウムを種晶とすることができ、あるいは、天然のリン鉱
石、骨炭などのリン酸カルシウムを主成分とする物質も
種晶とすることができる。さらに、砂などのろ材面に、
リン酸カルシウムを析出させた種晶も用いることができ
る。種晶としては、反応によって生成するリン酸カルシ
ウムと同種のリン酸カルシウムを主成分とするものであ
ることが好ましい。本発明装置の運転を開始する際に
は、晶析反応塔の下部に種晶を充填するとともに、混和
槽内のリン含有水にも種晶を添加する。混和槽を撹拌し
て種晶を水中にスラリー状に分散させ、リン含有水を送
り込み、所定量の水溶性カルシウム化合物を添加し、混
和槽の流出液のpHが所定の値になるようにpH調整剤を添
加する。混和槽の流出液は、流出液配管を通じて晶析反
応塔下部の流出液導入口に導く。晶析反応塔内には、種
晶充填層が形成されているので、リン酸カルシウムが過
飽和の状態となった混和槽の流出液は、種晶の表面にリ
ン酸カルシウムを晶析しつつ塔内を上向流で流れ、リン
濃度の低い処理水となって、塔上部に設けられた流出口
より流出する。混和槽の流出液に含まれて晶析反応塔に
運ばれた種晶は、晶析反応塔より混和槽に返送する。種
晶を混和槽に返送する方法に特に制限はなく、例えば、
ポンプを使用する方法、エアリフトによる方法などを用
いることができる。本発明装置の運転を長期間継続する
と、種晶の量が次第に増加するので、種晶の一部を適宜
系外に排出することが好ましい。種晶の一部を系外に排
出する方法に特に制限はなく、例えば、晶析反応塔の下
部に種晶排出口を設けることができ、あるいは、種晶返
送配管に分岐管を設けて排出することもできる。
[0007] The apparatus of the present invention incorporates a seed crystal in a crystallization reaction tower. The substance used as the seed crystal is a substance generated by the reaction between the phosphate group in the phosphorus-containing water and the added water-soluble calcium compound or a substance similar thereto, such as apatite such as hydroxyapatite, fluorapatite, and chloroapatite. Calcium phosphate such as tricalcium phosphate can be used as a seed crystal, or a substance containing calcium phosphate as a main component such as natural phosphate rock and bone charcoal can be used as a seed crystal. In addition, on the surface of filter media such as sand,
Seed crystals on which calcium phosphate is precipitated can also be used. It is preferable that the seed crystal is mainly composed of the same kind of calcium phosphate as calcium phosphate generated by the reaction. When the operation of the apparatus of the present invention is started, the lower part of the crystallization reaction tower is filled with a seed crystal, and the seed crystal is also added to the phosphorus-containing water in the mixing tank. Stir the mixing tank to disperse the seed crystals in water in a slurry state, feed in phosphorus-containing water, add a predetermined amount of a water-soluble calcium compound, and adjust the pH of the effluent of the mixing tank to a predetermined value. Add modifier. The effluent from the mixing tank is led to the effluent inlet at the bottom of the crystallization reaction tower through the effluent piping. Since a seed crystal packed bed is formed in the crystallization reaction tower, the effluent of the mixing tank in which calcium phosphate is supersaturated flows upward while crystallizing calcium phosphate on the surface of the seed crystal. It flows as a stream, becomes treated water with a low phosphorus concentration, and flows out from an outlet provided at the top of the tower. The seed crystals contained in the effluent of the mixing tank and carried to the crystallization reaction tower are returned from the crystallization reaction tower to the mixing tank. There is no particular limitation on the method of returning the seed crystal to the mixing tank, for example,
A method using a pump, a method using an air lift, and the like can be used. If the operation of the apparatus of the present invention is continued for a long period of time, the amount of seed crystals gradually increases. Therefore, it is preferable to appropriately discharge some of the seed crystals to the outside of the system. There is no particular limitation on the method of discharging a part of the seed crystal out of the system. For example, a seed crystal outlet can be provided at the lower part of the crystallization reaction tower, or a branch pipe is provided in the seed crystal return pipe to discharge the seed crystal. You can also.

【0008】本発明方法において、混和槽内の種晶濃度
は、1〜30重量%であることが好ましく、5〜20重
量%であることがより好ましい。混和槽内の種晶濃度が
1重量%未満であると、微細なリン酸カルシウムの粒子
が発生するおそれがある。混和槽内の種晶濃度が30重
量%を超えると、撹拌や移送に要する消費動力が大きく
なり、また、配管内に結晶が沈積するおそれがある。リ
ン酸カルシウム生成の反応速度は、カルシウムイオン濃
度とpHの少なくとも一方を高くすることにより増大する
が、前述のように微細な粒子生成を抑制するために、こ
れらの設定条件には制限がある。しかし、本発明におい
ては、混和槽に水溶性カルシウム化合物とpH調整剤を添
加するので、急速に撹拌して、これらの薬剤を速やかに
拡散させることができ、かつ種晶が存在するために、カ
ルシウムイオン濃度とpHを高くしても、リン酸カルシウ
ムの析出は種晶表面でおこり、微細な粒子の発生を抑制
することができる。また、混和槽では薬剤を拡散させる
ために完全混合状態となり、混和槽内の種晶は流出液と
ともに流出し、晶析反応塔へ流入するが、反応塔内は線
速度が低いために種晶は沈降し、処理水と種晶の固液分
離を容易に行うことができる。本発明方法において、種
晶の平均粒径に特に制限はないが、0.05〜1mmであ
ることが好ましく、0.1〜0.5mmであることがより好
ましい。種晶の平均粒径が0.05mm未満であると、完
全な固液分離が困難となって、微細な種晶が処理水に混
入するおそれがある。種晶の平均粒径が1mmを超える
と、リン酸カルシウムの析出がおこる表面積が小さくな
り、種晶の表面以外で微細な結晶が析出するおそれがあ
る。本発明のリン含有水の処理装置及び処理方法によれ
ば、混和槽内におけるカルシウムイオン濃度とpHを高め
ることができるので、処理水のリン濃度が所定濃度まで
到達する反応時間を短縮することができ、リン酸カルシ
ウム晶析反応塔からの微細なリン酸カルシウム粒子の流
出及び塔内でのスケール生成を防止し、リン含有水中の
リン酸根をリン酸カルシウムとして効果的に除去、回収
することができる。
In the method of the present invention, the seed crystal concentration in the mixing tank is preferably from 1 to 30% by weight, more preferably from 5 to 20% by weight. If the seed crystal concentration in the mixing tank is less than 1% by weight, fine calcium phosphate particles may be generated. If the seed crystal concentration in the mixing tank exceeds 30% by weight, the power consumption required for stirring and transfer increases, and crystals may be deposited in the piping. The reaction rate of calcium phosphate formation is increased by increasing at least one of the calcium ion concentration and the pH, but these setting conditions are limited in order to suppress the formation of fine particles as described above. However, in the present invention, since the water-soluble calcium compound and the pH adjuster are added to the mixing tank, these agents can be rapidly stirred to rapidly diffuse these agents, and since seed crystals are present, Even when the calcium ion concentration and the pH are increased, the precipitation of calcium phosphate occurs on the seed crystal surface, and the generation of fine particles can be suppressed. In addition, the mixing tank is in a completely mixed state to diffuse the drug, and the seed crystals in the mixing tank flow out together with the effluent and flow into the crystallization reaction tower. Precipitates, and solid-liquid separation of treated water and seed crystals can be easily performed. In the method of the present invention, the average grain size of the seed crystals is not particularly limited, but is preferably 0.05 to 1 mm, more preferably 0.1 to 0.5 mm. If the average particle size of the seed crystal is less than 0.05 mm, it is difficult to completely separate the solid and liquid, and there is a possibility that the fine seed crystal may be mixed into the treated water. If the average particle size of the seed crystal exceeds 1 mm, the surface area on which calcium phosphate is precipitated becomes small, and fine crystals may be deposited on the surface other than the surface of the seed crystal. According to the apparatus and method for treating phosphorus-containing water of the present invention, the calcium ion concentration and the pH in the mixing tank can be increased, so that the reaction time for the phosphorus concentration of the treated water to reach a predetermined concentration can be reduced. Thus, it is possible to prevent the outflow of fine calcium phosphate particles from the calcium phosphate crystallization reaction tower and the formation of scale in the tower, and to effectively remove and recover phosphate groups in the phosphorus-containing water as calcium phosphate.

【0009】[0009]

【実施例】以下に、実施例を挙げて本発明をさらに詳細
に説明するが、本発明はこれらの実施例によりなんら限
定されるものではない。なお、実施例及び比較例におい
て、リン酸イオンはJIS K 0102 46.1.1に
したがって定量し、全リンはJIS K 0102 46.
3.1にしたがって定量した。 実施例1 リン酸イオンをリンとして3mgP/L含有する原水を、
図1に類する装置を用い、リン灰石を種晶として脱リン
処理を行った。混和槽は容量100mLであり、混和槽中
のリン灰石の濃度が10重量%になるように、反応塔内
のリン灰石を返送した。反応塔は、直径30mm、高さ
2,000mmであり、平均粒径0.2mmのリン灰石を高さ
100mmまで充填した。混和槽に原水を7.5L/hr
(混和槽と反応塔の容積の合計に対しSV5hr-1)送り
込み、撹拌しつつ、塩化カルシウム水溶液をカルシウム
濃度が40mgCa/Lになるよう添加し、反応塔入口にお
いて水のpHが9.5になるように水酸化ナトリウム水溶
液を添加した。混和槽の流出液を、反応塔下部より反応
塔に送り込み、反応塔上部から処理水を流出させた。処
理水の水質は、全リン(T−P)0.4mg/L、リン酸
イオン性リン(PO4 3-−P)0.3mg/Lであった。 比較例1 反応塔から混和槽へのリン灰石の返送を行わない以外
は、実施例1と同様にして、脱リン処理を行った。すな
わち、リン酸イオンをリンとして3mgP/L含有する原
水を、混和槽に7.5L/hr送り込み、撹拌しつつ、塩
化カルシウム水溶液をカルシウム濃度が40mgCa/Lに
なるよう添加し、反応塔入口において水のpHが9.5に
なるように水酸化ナトリウム水溶液を添加した。混和槽
の流出液を、直径30mm、高さ2,000mmで、平均粒
径0.2mmのリン灰石を高さ100mmまで充填した反応
塔の下部より送り込み、反応塔上部から処理水を流出さ
せた。処理水の水質は、全リン(T−P)1.7mg/
L、リン酸イオン性リン(PO4 3-−P)0.4mg/Lで
あった。実施例1及び比較例1の結果を、第1表に示
す。
The present invention will be described in more detail with reference to the following examples.
However, the present invention is not limited to these examples.
It is not specified. In Examples and Comparative Examples,
The phosphate ion is compliant with JIS K 0102 46.1.1.
Therefore, it was quantified and total phosphorus was determined according to JIS K 0102 46.
Quantification according to 3.1. Example 1 Raw water containing 3 mg P / L of phosphate ions as phosphorus was
Dephosphorization using apatite as a seed crystal using an apparatus similar to Fig. 1.
Processing was performed. The mixing tank has a capacity of 100 mL and is inside the mixing tank.
In the reaction tower so that the concentration of apatite is 10% by weight.
Returned apatite. The reaction tower is 30mm in diameter and height
2,000 mm in height, apatite with an average particle size of 0.2 mm
Filled up to 100 mm. 7.5L / hr of raw water in mixing tank
(SV5hr for the total volume of mixing tank and reaction tower)-1) Feed
And agitate the aqueous calcium chloride solution
Add the solution to a concentration of 40 mg Ca / L, and add
Sodium hydroxide solution so that the pH of water becomes 9.5
The liquid was added. The effluent of the mixing tank is reacted from the bottom of the reaction tower
The water was sent to the tower, and treated water was allowed to flow out from the upper part of the reaction tower. place
The water quality of the water is 0.4 mg / L of total phosphorus (TP), phosphoric acid
Ionic phosphorus (POFour 3--P) 0.3 mg / L. Comparative Example 1 Except not returning apatite from the reaction tower to the mixing tank
Was subjected to a dephosphorization treatment in the same manner as in Example 1. sand
That is, a source containing 3 mg P / L of phosphate ions as phosphorus.
Water is fed into the mixing tank at a rate of 7.5 L / hr.
Calcium iodide aqueous solution with calcium concentration of 40mgCa / L
And adjust the pH of the water at the inlet of the reactor to 9.5.
An aqueous solution of sodium hydroxide was added to the mixture. Mixing tank
Effluent is 30 mm in diameter and 2,000 mm in height, average particle size
Reaction filled with apatite 0.2mm in diameter up to 100mm in height
Sent from the bottom of the tower, and the treated water
I let you. The quality of the treated water is 1.7 mg / kg of total phosphorus (TP).
L, phosphate ionic phosphorus (POFour 3--P) at 0.4 mg / L
there were. Table 1 shows the results of Example 1 and Comparative Example 1.
You.

【0010】[0010]

【表1】 [Table 1]

【0011】第1表に見られるように、反応塔内のリン
灰石を混和槽に返送した実施例1においては、処理水の
リン濃度が低く、リンが効果的に除去されている。これ
に対して、リン灰石の混和槽への返送を行わなかった比
較例1においては、リン酸イオン性リンの濃度は低下し
ているが、全リン濃度が高く、微細な粒子の生成が多い
ことが分かる。
As shown in Table 1, in Example 1 in which apatite in the reaction tower was returned to the mixing tank, the phosphorus concentration of the treated water was low, and phosphorus was effectively removed. On the other hand, in Comparative Example 1 in which the apatite was not returned to the mixing tank, the concentration of the phosphate ion phosphorus was reduced, but the total phosphorus concentration was high, and the generation of fine particles was reduced. You can see that there are many.

【0012】[0012]

【発明の効果】本発明のリン含有水の処理装置及び処理
方法によれば、リン酸カルシウム晶析反応塔からの微細
なリン酸カルシウム粒子の流出及び塔内でのスケール生
成を防止し、リン含有水中のリン酸根をリン酸カルシウ
ムとして効果的に除去、回収することができる。
According to the apparatus and method for treating phosphorus-containing water of the present invention, the outflow of fine calcium phosphate particles from the calcium phosphate crystallization reaction tower and the formation of scale in the tower are prevented, and the phosphorus in the phosphorus-containing water is prevented. The acid radical can be effectively removed and recovered as calcium phosphate.

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

【図1】図1は、本発明装置の一態様の工程系統図であ
る。
FIG. 1 is a process flow diagram of one embodiment of the apparatus of the present invention.

【符号の説明】[Explanation of symbols]

1 混和槽 2 晶析反応塔 3 種晶充填層 4 種晶返送配管 5 流出液配管 REFERENCE SIGNS LIST 1 mixing tank 2 crystallization reaction tower 3 seed crystal packed bed 4 seed crystal return pipe 5 effluent pipe

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】リン酸根を含有する水と水溶性カルシウム
化合物とpH調整剤との混和槽と、該混和槽の流出液の導
入口を塔下部に有し、処理水の流出口を塔上部に有し、
かつ種晶を内蔵する晶析反応塔とを備えたリン含有水の
処理装置において、前記晶析反応塔内の種晶を前記混和
槽に返送する種晶返送手段を有することを特徴とするリ
ン含有水の処理装置。
1. A mixing tank of water containing a phosphate group, a water-soluble calcium compound and a pH adjuster, an inlet for an effluent of the mixing tank at a lower part of the tower, and an outlet of treated water at an upper part of the tower. Have
A phosphorus-containing water treatment apparatus having a crystallization reaction tower having a built-in seed crystal and a seed crystal returning means for returning a seed crystal in the crystallization reaction tower to the mixing tank. Equipment for treating contained water.
【請求項2】リン酸根を含有する水に水溶性カルシウム
化合物とpH調整剤を添加し、リン化合物を晶析させて除
去するリン含有水の処理方法において、リン酸根を含有
する水と水溶性カルシウム化合物とpH調整剤とを、種晶
の存在下に混和槽において混和したのち、種晶を内蔵す
る晶析反応塔下部に導入し、リン化合物を晶析させつつ
晶析反応塔内に通水し、処理水を反応塔上部より流出さ
せるとともに、晶析反応塔内の種晶を混和槽に返送する
ことを特徴とするリン含有水の処理方法。
2. A method for treating phosphorus-containing water, wherein a water-soluble calcium compound and a pH adjuster are added to water containing a phosphate group to crystallize and remove the phosphorus compound. The calcium compound and the pH adjuster are mixed in a mixing tank in the presence of the seed crystal, and then introduced into the lower portion of the crystallization reaction tower containing the seed crystal.The phosphorus compound is crystallized while passing through the crystallization reaction tower. A method for treating phosphorus-containing water, comprising watering the treated water from the upper part of the reaction tower, and returning the seed crystals in the crystallization reaction tower to the mixing tank.
【請求項3】混和槽内の種晶濃度が1〜30重量%にな
るように、晶析反応塔内の種晶を混和槽に返送する請求
項2記載のリン含有水の処理方法。
3. The method for treating phosphorus-containing water according to claim 2, wherein the seed crystals in the crystallization reaction tower are returned to the mixing tank so that the seed crystals in the mixing tank have a concentration of 1 to 30% by weight.
JP2000136786A 2000-05-10 2000-05-10 Apparatus and method for treating phosphorus- containing water Pending JP2001314874A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000136786A JP2001314874A (en) 2000-05-10 2000-05-10 Apparatus and method for treating phosphorus- containing water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000136786A JP2001314874A (en) 2000-05-10 2000-05-10 Apparatus and method for treating phosphorus- containing water

Publications (1)

Publication Number Publication Date
JP2001314874A true JP2001314874A (en) 2001-11-13

Family

ID=18644673

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000136786A Pending JP2001314874A (en) 2000-05-10 2000-05-10 Apparatus and method for treating phosphorus- containing water

Country Status (1)

Country Link
JP (1) JP2001314874A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003190967A (en) * 2001-12-25 2003-07-08 Kurita Water Ind Ltd Crystallization and dephosphorization method and apparatus

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003190967A (en) * 2001-12-25 2003-07-08 Kurita Water Ind Ltd Crystallization and dephosphorization method and apparatus

Similar Documents

Publication Publication Date Title
JP3169899B2 (en) Method and apparatus for treating fluorine-containing wastewater
WO2006035834A1 (en) Method of treatment with reactional crystallization and apparatus therefor
JP2013246144A (en) Treatment method and treatment device for waste water containing radioactive strontium
US6210589B1 (en) Process for removing fluoride from wastewater
JP4519485B2 (en) Phosphorus recovery method and apparatus
JPH0712477B2 (en) How to remove phosphorus in water
JP4647640B2 (en) Crystallization reactor and crystallization reaction method
AU654449B2 (en) Process for the removal of phosphorous
JP2001314874A (en) Apparatus and method for treating phosphorus- containing water
JP4374825B2 (en) Crystalline dephosphorization method
JPH0512999B2 (en)
JP4337303B2 (en) How to remove sulfate ions
JPS6097090A (en) Treatment of water containing fluoride ion and sulfate ion
JPH01119392A (en) Treatment of waste water and equipment therefor
JP2002292202A (en) Crystallization reaction apparatus provided with means for recovering crystallization-reactive component
JP3341639B2 (en) How to remove phosphorus
JP2002292202A5 (en)
JP5162210B2 (en) Crystallization reactor and crystallization reaction method
JP4104874B2 (en) Crystallization method using calcium hydroxide
JP4211265B2 (en) Dephosphorization material
JP5421528B2 (en) Crystallization reactor and crystallization reaction method
JP2002102602A (en) Crystallization reaction device
JPS648598B2 (en)
JP2003126868A (en) Treating method of fluorine-containing water containing phosphoric acid ion and treating equipment
JP4649596B2 (en) Phosphorus removal method and phosphorus removal apparatus