JP3982881B2 - Treatment apparatus and treatment method for waste water containing phosphate ions - Google Patents

Treatment apparatus and treatment method for waste water containing phosphate ions Download PDF

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Publication number
JP3982881B2
JP3982881B2 JP22607097A JP22607097A JP3982881B2 JP 3982881 B2 JP3982881 B2 JP 3982881B2 JP 22607097 A JP22607097 A JP 22607097A JP 22607097 A JP22607097 A JP 22607097A JP 3982881 B2 JP3982881 B2 JP 3982881B2
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electrode
electrode pair
polarity
ions
adjacent electrodes
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JPH1157745A (en
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雅貴 森泉
明広 福本
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Sanyo Electric Co Ltd
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Sanyo Electric Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/463Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation

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  • Removal Of Specific Substances (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Description

【0001】
【発明の属する技術分野】
本発明は、排水、とくに家庭排水または集合住宅の排水などのリン酸イオンを含む生活排水の処理装置および処理方法に関する。
【0002】
【従来の技術】
川や湖の富栄養化の原因の1つにリン化合物の存在があることは周知である。また、このリン化合物は一般家庭の生活排水中に多く存在するが、浄化処理が困難なものであり、有効な対策がとれないのが現状である。
【0003】
リン化合物の処理装置は種々提案されているが、家庭排水については鉄の電解溶出法が知られている(特開平3−89998号公報)。この技術は、排水中のリン酸イオンを鉄イオンと反応させ水不溶性の塩、たとえばFePO4やFe(OH)x(PO4yとして凝集沈殿させて除去しようとする技術であり、電解槽中に設置された鉄製の電極に通電して排水中に鉄イオンを溶出させるものである。そして、かかる電界溶出法を用いた汚水処理装置として、たとえば嫌気槽、好気槽および処理水槽からなり、該処理水槽の汚水を、リン酸と反応する鉄イオンを溶出する処理装置を介して、嫌気槽に返送するように構成されたものがある。
【0004】
【発明が解決しようとする課題】
前記電解槽中に設置された電極のうち陽極側の電極は、通電により鉄イオンが溶出するため、該電極の厚さおよび幅が次第に減少する。かかる電極の厚さの減少度合(溶出量)は、対向して配置される電極間の電解面が大きく、該電極の電解面の反対側(裏面)は小さいため、電極の厚さは電解面側から減少し、早期に電極のかたべりを生じる。かかる電極のかたべりが生じると、陽極側の電極と陰極側の電極とのあいだの距離が大きくなり、電極に定電流を流すばあい、電圧が高くなり、消費電力が増加する。
【0005】
本発明は、叙上の事情に鑑み、電極の両面を溶解させることにより、消費電力を低減させることができるリン酸イオン含有排水の処理装置および処理方法を提供することを目的とする。
【0006】
【課題を解決するための手段】
本発明のリン酸イオン含有排水の処理装置は、排水の流入口と流出口を有する排水処理室と、該処理室内の排水中に少なくとも一部が浸漬するように配置され、鉄イオンおよび/またはアルミニウムイオン発生源を含んでいる電極と、該電極に通電するための電源とからなる排水の処理装置であって、少なくとも2対の電極が配置されており、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陽極にするとともに他方の電極を陰極にする構成と、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陰極にするとともに他方の電極を陽極にする構成と、各電極対の隣り合う電極の一方を陽極にするとともに他方を陰極にすることにより各電極対の隣り合う電極の極性を異極する構成と、各電極対の隣り合う電極の一方を陰極にするとともに他方を陽極にすることにより各電極対の隣り合う電極の極性を異極にする構成と、を繰り返す極性変換装置を備えてなることを特徴としている。
【0007】
また本発明のリン酸イオン含有排水の処理装置は、鉄イオンおよび/またはアルミニウムイオンを含む電極を用いてリン酸イオンを含む排水中に鉄イオンおよび/またはアルミニウムイオンを電気化学的に溶出させリン酸イオンを鉄および/またはアルミニウムとの不溶性塩の形で凝集沈殿させる排水の処理方法であって、排水中に少なくとも2対の電極が配置されており、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陽極にするとともに他方の電極を陰極にする構成と、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陰極にするとともに他方の電極を陽極にする構成と、各電極対の隣り合う電極の一方を陽極にするとともに他方を陰極にすることにより各電極対の隣り合う電極の極性を異極する構成と、各電極対の隣り合う電極の一方を陰極にするとともに他方を陽極にすることにより各電極対の隣り合う電極の極性を異極にする構成と、を繰り返すことを特徴としている。
【0008】
さらに本発明のリン酸イオン含有排水の処理装置は、鉄イオンおよび/またはアルミニウムイオンを含む電極を用いてリン酸イオンを含む排水中に鉄イオンおよび/またはアルミニウムイオンを電気化学的に溶出させリン酸イオンを鉄および/またはアルミニウムとの不溶性塩の形で凝集沈殿させる排水の処理方法であって、排水中に少なくとも2対の電極が配置されており、各電極対の隣り合う電極の極性を同極にし、ついで所定の電解時間が経過したのち、該各電極対内の電極の極性を変換し、ついで所定の電解時間が経過したのち、該各電極対の隣り合う電極の極性を異極に変換し、つぎに所定の電解時間が経過したのち、該各電極対の隣り合う電極の極性を変換することを特徴としている。
【0009】
【発明の実施の形態】
以下、添付図面に基づいて本発明のリン酸イオン含有排水の処理装置および処理方法を説明する。
【0010】
図1は本発明のリン酸イオン含有排水の処理装置の一実施の形態を示す説明図、図2は図1における処理装置の拡大図、図3は本発明の処理方法の一実施の形態を示す説明図である。
【0011】
本発明の処理装置は、たとえば合併浄化槽に用いられる。かかる合併浄化槽は、図1に示すように、第1嫌気ろ床槽Aと、第2嫌気ろ床槽Bと、生物ろ過槽Cと、処理水槽Dと、消毒槽Eとからなり、前記第1嫌気ろ床槽Aに流入した排水を各槽にて処理したのち、消毒槽Eから排出するようにされている。そして処理装置1が、前記処理水槽DからエアポンプFにより揚水された処理水を第1嫌気ろ床槽Aへ戻す循環経路に設置されている。
【0012】
前記処理装置1は、図1〜2に示すように、排水の流入口2と流出口3を有する排水処理室4と、該処理室4内の排水中に少なくとも一部が浸漬するように配置されている電極5、6と、該電極5、6に通電するための電源7と、電極5、6の電解を切り換えるための極性変換装置8と、前記排水処理室4内の排水中に空気を供給する空気ばっ気装置9を備えている。
【0013】
前記電極5、6は、鉄、鉄合金、アルミニウム、アルミニウム合金または鉄−アルミニウム合金などの鉄イオンおよび/またはアルミニウムイオン発生源から製作することができる。
【0014】
前記電極5、6は、図1〜2に示すように、電源7に対し、絶縁性支柱10により排水中に吊り下げられている。また該電極5、6には、端子11がネジ止またはハンダ付などにより固着されており、該端子11から引き出されたリード線12が電源7に接続されている。
【0015】
本実施の形態では、前記電極5、6は、排水中に3対A1、A2およびA3配置されており、電極5、6のうち、電極5が陽極(アノード)側の電極、電極6が陰極(カソード)側の電極にされている。また各電極対A1〜A3の隣り合う電極、すなわち電極対A1における電極6と電極対A2における電極6および電極対A2における電極5と電極対A3における電極5の極性が同極になるように配置されている。そして前記極性変換装置8により、各電極対A1〜A3内、隣接する電極対A1とA2および電極対A2とA3のあいだで行なわれる電解が切り換えられる。
【0016】
たとえば図3(a)〜(b)に示すように、所定の電解時間が経過したのち、各電極対A1〜A3内の電極5、6の極性を変換し、各電極対A1〜A3における電極5、6間で電解を継続する。ついで所定の電解時間が経過したのち、図3(c)に示すように、電極対A1と電極対A2の隣り合う電極6、6の極性を異なる極性に変換するとともに、電極対A2と電極対A3の隣り合う電極5、5の極性を異なる極性に変換し、電解する面を変更する。なお、このときの電極対A1における電極5と電極対A3における電極6には、異なる極性を持つ電極を持たないため、通電が停止される。つぎに所定の電解時間が経過したのち、図3(d)に示すように、電極対A1と電極対A2の隣り合う電極6、6の極性を異なる極性に変換するとともに、電極対A2と電極対A3の隣り合う電極5、5の極性を異なる極性に変換し、電解を継続する。ついで所定の電解時間が経過したのち、図3(a)に示すように、最初の各電極対A1〜A3の隣り合う電極の極性を同極に変換する。
【0017】
これまでの電極の極性変換の操作を1サイクルとし、引き続き電解を行なう。
【0018】
なお、前記所定の電解時間としては、10分未満では溶出効率が低下するため、10分以上、好ましくは30分以上とすることができる。また本実施の形態では、排水中に3対の電極が配置されているが、本発明おいては、これに限定されるものではなく、排水中に2対または4対以上の電極を配置することができる。
【0019】
本実施の形態では、電極の電解を交互に両面で行なうため、電極間距離が大きくなることを防ぐことができ、消費電力の増加を防止することができるとともに、酸化物などの付着物が付きにくくなり、溶出量が低減しない。さらに各電極対のあいだの距離を従来より小さくできるため、処理装置をコンパクトにすることができる。
【0020】
前記空気ばっ気装置9は、排水処理室4の底中央に設置される多孔質の散気管13または散気板と、該散気管13に圧縮空気を吸き込むためのエアポンプ14とから構成されており、前記散気管13とエアポンプ14はパイプ15により接続されている。
【0021】
本実施の形態では、前記散気管13は排水処理室4の底中央に設置されているが、本発明においては、とくにこれに限定されるものではなく、排水を撹拌し、排水の流出とともに、排水中のリン酸イオンと電極から溶出した鉄イオン(アルミニウムイオン)との反応生成物である水不溶性の塩を流出させやすい位置を適宜選定して設置することができる。たとえば前記散気管13は、排水処理室4の流出口3側の壁4aに対して垂直に設置されているが、散気管13を壁4aに近づけ、かつ壁4aに対して平行、すなわち図1の紙面垂直方向にするとともに、少し底から高い位置に配置することにより、処理室内の排水の対流を生じやすくする。また、散気管を処理室内の排水中で上下方向に動かすことで排水の対流を生じやすくすることもできる。なお、本実施の形態では、前記排水の撹拌により、鉄イオンとリン酸イオンとの反応性を向上させることもできる。
【0022】
鉄(アルミニウム)の電解溶出法には、従来公知の方法が採用でき、電極への通電は連続的でも断続的、パルス的でもよい。通電量はリン酸イオンや他のイオンの濃度、排水の流量などによって異なるが、鉄イオンおよび/またはアルミニウムイオンの排水中の濃度/リン酸イオン濃度の比(以下、「Fe/P」と略す)が0.8〜3.0、好ましくは1.0〜2.5となるように調節すればよい。
【0023】
本発明における、リン酸イオン含有排水の鉄(アルミニウム)の電解溶出法による処理は、電極から溶出した鉄イオン(アルミニウムイオン)が排水中のリン酸イオンと反応して水不溶性のリン酸と鉄(アルミニウム)との塩を生成させる反応(反応A)を利用するものであるが、排水中は水酸イオンが存在しており、溶出した鉄イオン(アルミニウムイオン)は水酸イオンとも反応する(反応B)。反応Bは反応Aよりも速いので、リン酸イオンを捕捉するためには電流量を多くして鉄イオン(アルミニウムイオン)の溶出量を増す必要がある。
【0024】
しかしながら、排水中にカルシウムイオンまたはマグネシウムイオンが存在すると、それらのイオンは水酸イオンと反応する(反応D)。この反応Dは鉄イオン(アルミニウムイオン)と水酸イオンとの反応Bに優先するため、反応Bが抑制され、鉄イオン(アルミニウムイオン)はリン酸イオンとの反応Aに有効に利用される。さらに、カルシウムイオンおよびマグネシウムイオンもリン酸イオンと反応して水不溶性の塩を形成するので、リン酸イオンの除去に貢献する。
【0025】
このため、本発明では、カルシウムイオンまたはマグネシウムイオンを添加し、鉄イオン(アルミニウムイオン)と水酸イオンの反応Bを抑制し、鉄イオン(アルミニウムイオン)とリン酸イオンの反応Aを効率よく行なわせることもできる。これにより、通電量を低減することができ、節電できるとともに鉄やアルミニウムの溶出量を低減できる。
【0026】
本発明の排水の処理装置は前述のように一般家庭排水にとくに有利に利用できる。したがって、単独で使用してもよいが、他の浄化システム、たとえば活性汚泥法、膜分離法、嫌気・好気循環法などと組合せて家庭用、集合住宅用の総合排水浄化システムとすることができる。また、大規模処理システム(し尿処理場)にも利用できる。
【0027】
つぎに本発明を実施例に基づいて説明するが、本発明はかかる実施例のみに限定されるものではない。
【0028】
実施例
図1に示す鉄の電解溶出排水処理装置を用い、流入口からリン酸イオン濃度5mg/リットル(H3PO4として添加)、Na+200mg/リットルおよびCa2+20mg/リットルを含む供試排水を流速1リットル/minで流入させた。
【0029】
排水中に浸漬させる3対の電極としては、高純度の鉄板を用いた。そして図3に示すように、電極の電解を両面で行なうように制御した。このときの通電時間は30分であり、電極への通電量はFe/Pが1.5となるように1.2Aとした。
【0030】
そして電極の電気分解により、溶出した鉄イオンはリン酸イオンと反応して水不溶性の塩が生成される。生成された塩は流入水とともに、散気管から発生する空気(2リットル/min)で撹拌され、流出側へと流れ出る。したがって、水不溶性の塩の堆積はほとんどなかった。
【0031】
ついで流出口で採取した排水を孔径0.45μmのフィルターで濾過した濾液をJIS K 0102に規格された全リン分析法(46.3)に準拠して調べた結果、リンの除去効率が90%以上であることがわかった。
【0032】
【発明の効果】
以上説明したとおり、本発明によれば、電極対の両サイドの電極を除き、電極の両面が均一に溶解するため、電極間距離が大きくなるとを防ぐことができ、消費電力の増加を防止することができる。
【図面の簡単な説明】
【図1】本発明のリン酸イオン含有排水の処理装置の一実施の形態を示す説明図である。
【図2】図1における処理装置の拡大図である。
【図3】本発明の処理方法の一実施の形態を示す説明図である。
【符号の説明】
1 処理装置
2 流入口
3 流出口
4 処理室
5、6 電極
7 電源
8 極性変換装置
9 空気ばっ気装置
10 絶縁性支柱
11 端子
12 リード線
[0001]
BACKGROUND OF THE INVENTION
TECHNICAL FIELD The present invention relates to a treatment apparatus and a treatment method for domestic wastewater containing phosphate ions such as wastewater, particularly domestic wastewater or apartment house wastewater.
[0002]
[Prior art]
It is well known that the presence of phosphorus compounds is one of the causes of eutrophication of rivers and lakes. Moreover, although this phosphorus compound exists abundantly in the domestic household wastewater, the present condition is that the purification process is difficult and an effective measure cannot be taken.
[0003]
Various treatment apparatuses for phosphorus compounds have been proposed, but an iron electrolysis method is known for domestic wastewater (Japanese Patent Laid-Open No. 3-89998). This technique is a technique in which phosphate ions in waste water are reacted with iron ions to coagulate and remove them as water-insoluble salts such as FePO 4 and Fe (OH) x (PO 4 ) y. An iron electrode installed inside is energized to elute iron ions into the waste water. And as a sewage treatment apparatus using such an electric field elution method, for example, an anaerobic tank, an aerobic tank, and a treated water tank, the sewage in the treated water tank is passed through a treatment apparatus that elutes iron ions that react with phosphoric acid, Some are configured to be returned to an anaerobic tank.
[0004]
[Problems to be solved by the invention]
Among the electrodes installed in the electrolytic cell, the anode-side electrode elutes iron ions when energized, so that the thickness and width of the electrode gradually decrease. The degree of decrease in the electrode thickness (elution amount) is such that the electrolysis surface between the electrodes arranged facing each other is large, and the opposite side (back surface) of the electrode electrolysis surface is small. Decrease from the side, causing electrode sticking early. When such electrode slippage occurs, the distance between the anode-side electrode and the cathode-side electrode increases, and when a constant current is passed through the electrode, the voltage increases and the power consumption increases.
[0005]
An object of this invention is to provide the processing apparatus and the processing method of the phosphate ion containing waste water which can reduce power consumption by dissolving both surfaces of an electrode in view of the above situation.
[0006]
[Means for Solving the Problems]
Processor phosphate ion-containing waste water of the present invention, a waste water treatment chamber having an inlet and an outlet of the drain, at least part of which is arranged to dip in the waste water of the processing chamber, iron ions and / Or a wastewater treatment apparatus comprising an electrode including an aluminum ion generation source and a power source for energizing the electrode, wherein at least two pairs of electrodes are disposed , and adjacent electrodes of each electrode pair A configuration in which the polarity is the same polarity and one electrode in each electrode pair is an anode and the other electrode is a cathode, and the polarity of adjacent electrodes in each electrode pair is the same polarity and one electrode in each electrode pair is A configuration in which the other electrode is an anode and the other electrode is an anode, and a configuration in which the polarity of the adjacent electrodes of each electrode pair is different by making one of the adjacent electrodes of each electrode pair an anode and the other a cathode , For each electrode pair Constitutes the to different pole polarity of adjacent electrodes of each electrode pair, characterized in that it comprises a polarity converter repeating by the anode and the other as well as to the cathode one electrode fit Ri.
[0007]
Further, the apparatus for treating wastewater containing phosphate ions of the present invention uses an electrode containing iron ions and / or aluminum ions to electrochemically elute iron ions and / or aluminum ions into wastewater containing phosphate ions. A wastewater treatment method for coagulating and precipitating acid ions in the form of an insoluble salt with iron and / or aluminum, wherein at least two pairs of electrodes are disposed in the wastewater, and the polarity of the adjacent electrodes of each electrode pair is determined. A configuration in which one electrode in each electrode pair is an anode and the other electrode is a cathode, and the polarity of adjacent electrodes in each electrode pair is the same polarity, and one electrode in each electrode pair is a cathode In addition, the polarity of the adjacent electrode of each electrode pair by making the other electrode an anode and making one of the adjacent electrodes of each electrode pair an anode and the other a cathode As a feature structure and the different pole, configurations and to different pole polarity of adjacent electrodes of each electrode pair by the other as well as to the cathode either the adjacent electrodes of each electrode pair to the anode, repeating the Yes.
[0008]
Furthermore, the phosphate ion-containing wastewater treatment apparatus according to the present invention uses an electrode containing iron ions and / or aluminum ions to electrochemically elute iron ions and / or aluminum ions into the wastewater containing phosphate ions. A wastewater treatment method for coagulating and precipitating acid ions in the form of an insoluble salt with iron and / or aluminum, wherein at least two pairs of electrodes are disposed in the wastewater, and the polarity of the adjacent electrodes of each electrode pair is determined. After the predetermined electrolysis time has elapsed, the polarity of the electrodes in each electrode pair is converted, and after the predetermined electrolysis time has elapsed, the polarities of the adjacent electrodes of each electrode pair are made different from each other. Then, after a predetermined electrolysis time has elapsed, the polarity of the adjacent electrodes of each electrode pair is converted.
[0009]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, the processing apparatus and the processing method of the phosphate ion containing waste_water | drain of this invention are demonstrated based on an accompanying drawing.
[0010]
FIG. 1 is an explanatory view showing an embodiment of a treatment apparatus for phosphate ion-containing waste water of the present invention, FIG. 2 is an enlarged view of the treatment apparatus in FIG. 1, and FIG. 3 is an embodiment of the treatment method of the present invention. It is explanatory drawing shown.
[0011]
The processing apparatus of this invention is used for a merged septic tank, for example. As shown in FIG. 1, the combined septic tank comprises a first anaerobic filter bed tank A, a second anaerobic filter bed tank B, a biological filter tank C, a treated water tank D, and a disinfection tank E. 1 Anaerobic filter The waste water flowing into the floor tank A is treated in each tank and then discharged from the disinfection tank E. And the processing apparatus 1 is installed in the circulation path which returns the treated water pumped up by the air pump F from the said treated water tank D to the 1st anaerobic filter bed tank A.
[0012]
As shown in FIGS. 1 and 2, the treatment apparatus 1 is disposed such that a wastewater treatment chamber 4 having a drainage inlet 2 and a drainage outlet 3 and at least a part of the wastewater in the treatment chamber 4 is immersed in the wastewater. Electrodes 5, 6, a power source 7 for energizing the electrodes 5, 6, a polarity conversion device 8 for switching the electrolysis of the electrodes 5, 6, and air in the waste water in the waste water treatment chamber 4 Is provided with an air aeration device 9 for supplying air.
[0013]
The electrodes 5, 6 can be fabricated from iron ions and / or aluminum ion sources such as iron, iron alloy, aluminum, aluminum alloy or iron-aluminum alloy.
[0014]
As shown in FIGS. 1 and 2, the electrodes 5 and 6 are suspended in the drainage by the insulating support column 10 with respect to the power source 7. Further, a terminal 11 is fixed to the electrodes 5 and 6 by screwing or soldering, and a lead wire 12 drawn from the terminal 11 is connected to a power source 7.
[0015]
In this embodiment, the electrodes 5 and 6 are arranged in three pairs A1, A2 and A3 in the waste water. Among the electrodes 5 and 6, the electrode 5 is an anode (anode) side electrode, and the electrode 6 is a cathode. The electrode is on the (cathode) side. Also, the electrodes adjacent to each of the electrode pairs A1 to A3, that is, the electrode 6 in the electrode pair A1 and the electrode 6 in the electrode pair A2, and the electrode 5 in the electrode pair A2 and the electrode 5 in the electrode pair A3 are arranged in the same polarity. Has been. The polarity conversion device 8 switches the electrolysis performed between the electrode pairs A1 to A3 and between the electrode pairs A1 and A2 and the electrode pairs A2 and A3.
[0016]
For example, as shown in FIGS. 3A to 3B, after a predetermined electrolysis time has elapsed, the polarities of the electrodes 5 and 6 in the electrode pairs A1 to A3 are converted, and the electrodes in the electrode pairs A1 to A3 are converted. Continue electrolysis between 5 and 6. Then, after a predetermined electrolysis time has elapsed, as shown in FIG. 3C, the polarities of the adjacent electrodes 6 and 6 of the electrode pair A1 and the electrode pair A2 are changed to different polarities, and the electrode pair A2 and the electrode pair are converted. The polarity of adjacent electrodes 5 and 5 of A3 is converted to a different polarity, and the surface to be electrolyzed is changed. In addition, since the electrode 5 in the electrode pair A1 and the electrode 6 in the electrode pair A3 at this time do not have electrodes having different polarities, energization is stopped. Next, after a predetermined electrolysis time has elapsed, as shown in FIG. 3D, the polarities of the adjacent electrodes 6 and 6 of the electrode pair A1 and the electrode pair A2 are changed to different polarities, and the electrode pair A2 and the electrode The polarity of the adjacent electrodes 5 and 5 of the pair A3 is changed to a different polarity, and electrolysis is continued. Next, after a predetermined electrolysis time has elapsed, as shown in FIG. 3A, the polarities of the adjacent electrodes of the first electrode pairs A1 to A3 are converted to the same polarity.
[0017]
The conventional electrode polarity conversion operation is one cycle and the electrolysis is continued.
[0018]
The predetermined electrolysis time can be set to 10 minutes or longer, preferably 30 minutes or longer, since elution efficiency decreases when it is less than 10 minutes. In this embodiment, three pairs of electrodes are disposed in the waste water. However, the present invention is not limited to this, and two pairs or four or more electrodes are disposed in the waste water. be able to.
[0019]
In this embodiment, since the electrodes are electrolyzed alternately on both sides, the distance between the electrodes can be prevented from increasing, power consumption can be prevented from increasing, and deposits such as oxides are attached. It becomes difficult and the amount of elution is not reduced. Furthermore, since the distance between each electrode pair can be made smaller than before, the processing apparatus can be made compact.
[0020]
The air aeration apparatus 9 includes a porous air diffusion tube 13 or an air diffusion plate installed at the bottom center of the waste water treatment chamber 4 and an air pump 14 for sucking compressed air into the air diffusion tube 13. The air diffuser 13 and the air pump 14 are connected by a pipe 15.
[0021]
In the present embodiment, the air diffuser 13 is installed in the center of the bottom of the waste water treatment chamber 4, but in the present invention, the present invention is not particularly limited to this. A position where water-insoluble salt, which is a reaction product of phosphate ions in the waste water and iron ions (aluminum ions) eluted from the electrodes, can be easily selected and installed. For example, the air diffuser 13 is installed perpendicular to the wall 4a on the outlet 3 side of the waste water treatment chamber 4, but the air diffuser 13 is close to the wall 4a and parallel to the wall 4a, that is, FIG. In addition to the vertical direction of the paper surface, it is arranged at a slightly higher position from the bottom to facilitate convection of the waste water in the processing chamber. Further, the convection of the waste water can be easily generated by moving the diffuser pipe vertically in the waste water in the processing chamber. In the present embodiment, the reactivity of iron ions and phosphate ions can be improved by stirring the waste water.
[0022]
A conventionally known method can be adopted as the electrolytic elution method for iron (aluminum), and the electrode may be energized continuously, intermittently, or pulsed. The amount of energization varies depending on the concentration of phosphate ions and other ions, the flow rate of wastewater, etc., but the ratio of the concentration of iron ions and / or aluminum ions in the wastewater / phosphate ion concentration (hereinafter abbreviated as “Fe / P”). ) May be adjusted to 0.8 to 3.0, preferably 1.0 to 2.5.
[0023]
In the present invention, the treatment by the electrolytic elution method of iron (aluminum) of the phosphate ion-containing wastewater is carried out by reacting the iron ion (aluminum ion) eluted from the electrode with the phosphate ion in the wastewater to form water-insoluble phosphoric acid and iron. Although a reaction (reaction A) that forms a salt with (aluminum) is utilized, hydroxide ions are present in the waste water, and the eluted iron ions (aluminum ions) also react with the hydroxide ions ( Reaction B). Since reaction B is faster than reaction A, in order to capture phosphate ions, it is necessary to increase the amount of current and increase the elution amount of iron ions (aluminum ions).
[0024]
However, when calcium ions or magnesium ions are present in the waste water, these ions react with hydroxide ions (Reaction D). Since this reaction D has priority over reaction B between iron ions (aluminum ions) and hydroxide ions, reaction B is suppressed, and iron ions (aluminum ions) are effectively used for reaction A with phosphate ions. Furthermore, calcium ions and magnesium ions also react with phosphate ions to form water-insoluble salts, thus contributing to the removal of phosphate ions.
[0025]
For this reason, in this invention, calcium ion or magnesium ion is added, reaction B of iron ion (aluminum ion) and hydroxide ion is suppressed, and reaction A of iron ion (aluminum ion) and phosphate ion is efficiently performed. It can also be made. Thereby, the amount of energization can be reduced, power can be saved, and the elution amount of iron and aluminum can be reduced.
[0026]
As described above, the wastewater treatment apparatus of the present invention can be used particularly advantageously for general household wastewater. Therefore, it may be used alone, but it can be combined with other purification systems such as activated sludge method, membrane separation method, anaerobic / aerobic circulation method, etc. to make a comprehensive wastewater purification system for households and collective housing. it can. It can also be used in large-scale processing systems (human waste treatment plants).
[0027]
Next, the present invention will be described based on examples, but the present invention is not limited to such examples.
[0028]
EXAMPLE Using an iron electrolysis elution waste water treatment apparatus shown in FIG. 1, a phosphate ion concentration of 5 mg / liter (added as H 3 PO 4 ), Na + 200 mg / liter and Ca 2+ 20 mg / liter is supplied from the inlet. The test wastewater was introduced at a flow rate of 1 liter / min.
[0029]
High purity iron plates were used as the three pairs of electrodes immersed in the waste water. Then, as shown in FIG. 3, the electrode was controlled to be electrolyzed on both sides. The energization time at this time was 30 minutes, and the energization amount to the electrode was 1.2 A so that Fe / P was 1.5.
[0030]
Then, by electrolysis of the electrode, the eluted iron ions react with phosphate ions to produce water-insoluble salts. The generated salt is stirred together with the inflowing water by the air (2 liter / min) generated from the air diffuser and flows out to the outflow side. Therefore, there was almost no accumulation of water-insoluble salts.
[0031]
Next, as a result of examining the filtrate obtained by filtering the waste water collected at the outlet with a filter having a pore diameter of 0.45 μm in accordance with the total phosphorus analysis method (46.3) standardized in JIS K 0102, the removal efficiency of phosphorus was 90%. It turns out that it is above.
[0032]
【The invention's effect】
As described above, according to the present invention, since both surfaces of the electrodes are uniformly dissolved except for the electrodes on both sides of the electrode pair, it is possible to prevent the distance between the electrodes from increasing and prevent an increase in power consumption. be able to.
[Brief description of the drawings]
FIG. 1 is an explanatory view showing an embodiment of a treatment apparatus for phosphate ion-containing waste water of the present invention.
FIG. 2 is an enlarged view of the processing apparatus in FIG.
FIG. 3 is an explanatory diagram showing an embodiment of a processing method of the present invention.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Processing apparatus 2 Inlet 3 Outlet 4 Processing chamber 5, 6 Electrode 7 Power supply 8 Polarity conversion apparatus 9 Air aeration apparatus 10 Insulating support | pillar 11 Terminal 12 Lead wire

Claims (4)

排水の流入口と流出口を有する排水処理室と、該処理室内の排水中に少なくとも一部が浸漬するように配置され、鉄イオンおよび/またはアルミニウムイオン発生源を含んでいる電極と、該電極に通電するための電源とからなる排水の処理装置であって、少なくとも2対の電極が配置されており、
各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陽極にするとともに他方の電極を陰極にする構成と、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陰極にするとともに他方の電極を陽極にする構成と、各電極対の隣り合う電極の一方を陽極にするとともに他方を陰極にすることにより各電極対の隣り合う電極の極性を異極する構成と、各電極対の隣り合う電極の一方を陰極にするとともに他方を陽極にすることにより各電極対の隣り合う電極の極性を異極にする構成と、を繰り返す極性変換装置を備えてなるリン酸イオン含有排水の処理装置。
A waste water treatment chamber having a waste water inlet and a water outlet, an electrode disposed at least partially immersed in waste water in the treatment chamber, and containing an iron ion and / or aluminum ion source; A wastewater treatment apparatus comprising a power source for energizing the electrodes, wherein at least two pairs of electrodes are disposed,
A configuration in which the polarity of adjacent electrodes of each electrode pair is the same polarity, and one electrode in each electrode pair is an anode and the other electrode is a cathode, and the polarity of adjacent electrodes in each electrode pair is the same polarity; A structure in which one electrode in each electrode pair is used as a cathode and the other electrode is used as an anode, and one of adjacent electrodes in each electrode pair is used as an anode and the other is used as a cathode so that adjacent electrodes of each electrode pair The polarity that repeats the configuration of making the polarity of each electrode pair different and the configuration that makes the polarity of the adjacent electrodes of each electrode pair different from each other by using one of the adjacent electrodes of each electrode pair as a cathode and the other as an anode An apparatus for treating wastewater containing phosphate ions, comprising a conversion device.
鉄イオンおよび/またはアルミニウムイオンを含む電極を用いてリン酸イオンを含む排水中に鉄イオンおよび/またはアルミニウムイオンを電気化学的に溶出させリン酸イオンを鉄および/またはアルミニウムとの不溶性塩の形で凝集沈殿させる排水の処理方法であって、排水中に少なくとも2対の電極が配置されており、
各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陽極にするとともに他方の電極を陰極にする構成と、各電極対の隣り合う電極の極性を同極にし且つ各電極対内の一方の電極を陰極にするとともに他方の電極を陽極にする構成と、各電極対の隣り合う電極の一方を陽極にするとともに他方を陰極にすることにより各電極対の隣り合う電極の極性を異極する構成と、各電極対の隣り合う電極の一方を陰極にするとともに他方を陽極にすることにより各電極対の隣り合う電極の極性を異極にする構成と、を繰り返すリン酸イオン含有排水の処理方法。
Using an electrode containing iron ions and / or aluminum ions, iron ions and / or aluminum ions are electrochemically eluted into waste water containing phosphate ions, and phosphate ions are in the form of insoluble salts with iron and / or aluminum. The wastewater treatment method for coagulating and precipitating with at least two pairs of electrodes disposed in the wastewater,
A configuration in which the polarity of adjacent electrodes of each electrode pair is the same polarity, and one electrode in each electrode pair is an anode and the other electrode is a cathode, and the polarity of adjacent electrodes in each electrode pair is the same polarity; A structure in which one electrode in each electrode pair is used as a cathode and the other electrode is used as an anode, and one of adjacent electrodes in each electrode pair is used as an anode and the other is used as a cathode so that adjacent electrodes of each electrode pair A configuration in which the polarities of the adjacent electrodes of each electrode pair are different from each other, and a configuration in which the polarity of the adjacent electrodes of each electrode pair is made different from each other by making one of the adjacent electrodes of each electrode pair a cathode and the other an anode. Treatment method for waste water containing acid ions.
鉄イオンおよび/またはアルミニウムイオンを含む電極を用いてリン酸イオンを含む排水中に鉄イオンおよび/またはアルミニウムイオンを電気化学的に溶出させリン酸イオンを鉄および/またはアルミニウムとの不溶性塩の形で凝集沈殿させる排水の処理方法であって、排水中に少なくとも2対の電極が配置されており、各電極対の隣り合う電極の極性を同極にし、ついで所定の電解時間が経過したのち、該各電極対内の電極の極性を変換し、ついで所定の電解時間が経過したのち、該各電極対の隣り合う電極の極性を異極に変換し、つぎに所定の電解時間が経過したのち、該各電極対の隣り合う電極の極性を変換するリン酸イオン含有排水の処理方法。  Using an electrode containing iron ions and / or aluminum ions, iron ions and / or aluminum ions are eluted electrochemically into waste water containing phosphate ions, and phosphate ions are in the form of insoluble salts with iron and / or aluminum. In the wastewater treatment method for coagulating sedimentation, at least two pairs of electrodes are arranged in the wastewater, the polarities of the adjacent electrodes of each electrode pair are made the same polarity, and then a predetermined electrolysis time has passed, The polarity of the electrodes in each electrode pair is converted, and then after a predetermined electrolysis time has elapsed, the polarity of the adjacent electrodes of each electrode pair is converted to a different polarity, and then after a predetermined electrolysis time has elapsed, A method for treating phosphate ion-containing wastewater that converts the polarity of adjacent electrodes of each electrode pair. 前記各電極対の隣り合う電極の極性を異極に変換するとき、両サイドの電極の通電を停止する請求項3記載の処理方法。  The processing method according to claim 3, wherein energization of the electrodes on both sides is stopped when the polarity of adjacent electrodes of each electrode pair is converted to a different polarity.
JP22607097A 1997-08-22 1997-08-22 Treatment apparatus and treatment method for waste water containing phosphate ions Expired - Fee Related JP3982881B2 (en)

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