JP2001038370A - Waste water treatment device - Google Patents

Waste water treatment device

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Publication number
JP2001038370A
JP2001038370A JP11220153A JP22015399A JP2001038370A JP 2001038370 A JP2001038370 A JP 2001038370A JP 11220153 A JP11220153 A JP 11220153A JP 22015399 A JP22015399 A JP 22015399A JP 2001038370 A JP2001038370 A JP 2001038370A
Authority
JP
Japan
Prior art keywords
phosphorus
tank
solid
sludge
liquid
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
JP11220153A
Other languages
Japanese (ja)
Other versions
JP4439040B2 (en
Inventor
Tatsuhiko Suzuki
辰彦 鈴木
Masaaki Yoshino
正章 吉野
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.)
Maezawa Industries Inc
Original Assignee
Maezawa Industries Inc
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 Maezawa Industries Inc filed Critical Maezawa Industries Inc
Priority to JP22015399A priority Critical patent/JP4439040B2/en
Publication of JP2001038370A publication Critical patent/JP2001038370A/en
Application granted granted Critical
Publication of JP4439040B2 publication Critical patent/JP4439040B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To efficiently remove phosphorus in sludge generating by treatment by sewerage, to reduce the burden of a waste water treatment equipment, and to prevent inflow of phosphorus into a secondary treatment water. SOLUTION: This device is provided with a solid liquid separation tank 10 for settling and separating solids in phosphorus-containing sludge, and a dephosphorizing tank 20 in which a dephosphorizing agent and calcium ions are added to the separation liquid from which the solids separated in the solid liquid separation tank 10 and phosphorus in the separation liquid is allowed to react with the added calcium to deposit solids and then phosphorus is removed from the separation liquid.

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、排水処理装置に関
し、詳しくは、生物脱リン法によるリンを高濃度に含有
した汚泥や、嫌気性消化汚泥中に含まれるオルトリン酸
イオン態リンを除去して汚泥返流水中のリンの濃度を低
下させ、生物脱リン法による排水処理を安定した状態で
行うための排水処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater treatment apparatus, and more particularly to a biological dephosphorization method for removing sludge containing a high concentration of phosphorus and orthophosphate ionic phosphorus contained in anaerobic digested sludge. The present invention relates to a wastewater treatment apparatus for reducing the concentration of phosphorus in sludge return water and performing wastewater treatment by a biological phosphorus removal method in a stable state.

【0002】[0002]

【従来の技術】下水の処理によって発生する汚泥は、有
機物を多く含有しており、放置すれば腐敗して悪臭を発
するなどの問題を起こすため、分解、無機化して、その
質の安定を図る必要がある。
2. Description of the Related Art Sludge generated by the treatment of sewage contains a large amount of organic substances, and if left untreated, causes a problem such as decay and gives off a bad smell. There is a need.

【0003】汚泥の嫌気性消化は、嫌気性微生物の働き
により、汚泥中の有機物を分解し、メタンガスを発生さ
せるものであって、メタンを回収することでエネルギー
回収の面からも意義あるものである。しかしながら、処
理後の汚泥、即ち消化汚泥中には、アンモニア性窒素、
オルトリンが高濃度に含まれており、これらは、返送先
で十分に除去できないため、二次処理水中への放出が懸
念されている。
[0003] Anaerobic digestion of sludge decomposes organic substances in sludge by the action of anaerobic microorganisms to generate methane gas, and is significant from the viewpoint of energy recovery by recovering methane. is there. However, the sludge after treatment, that is, digested sludge, contains ammonia nitrogen,
Orthrin is contained in a high concentration, which cannot be sufficiently removed at the return destination, and there is a concern about release into secondary treatment water.

【0004】一方、消化汚泥は、汚泥中のマグネシウム
イオンと反応し、消化汚泥管壁面でリン酸マグネシウム
アンモニウム六水和物のスケールを生成し、消化汚泥管
の閉塞の原因となっている。これは脱水装置内でも進行
し、例えばベルトプレスのろ布の目詰まりの進行を早め
たり、遠心脱水機のボール内壁面でスケールを生成させ
たりするため、維持管理上大きな問題となっている。
[0004] On the other hand, digested sludge reacts with magnesium ions in the sludge to form scale of magnesium ammonium phosphate hexahydrate on the wall surface of the digested sludge tube, causing blockage of the digested sludge tube. This also progresses in the dewatering device, and for example, hastening the progress of clogging of the filter cloth of the belt press and generating scale on the inner wall surface of the ball of the centrifugal dewatering machine, thus causing a serious problem in maintenance.

【0005】また、好気性消化は、散気式又は機械撹拌
式エアレーションによって汚泥を好気性状態に保ち、有
機物を酸化分解して汚泥を安定化するものである。この
方法は、酸素供給が必要なため、運転費が高いなどの短
所があり、これまで我が国においては実施例が少ないも
のの、運転操作が容易であり、悪臭が少ないなどの長所
から、今後は、小規模下水処理向けに普及する可能性が
残されている。ところが、この方法においても、消化汚
泥脱水ろ液中に高濃度のオルトリンが含まれており、こ
れが水処理系に再び戻されることにより、負荷が増大
し、二次処理水質の悪化の一因となる。
In aerobic digestion, sludge is kept in an aerobic state by aeration or mechanical stirring aeration, and organic matter is oxidized and decomposed to stabilize the sludge. This method has drawbacks such as high operating costs due to the need for oxygen supply.Although there are few examples in Japan so far, the driving operation is easy and there are few bad smells. The potential remains widespread for small-scale sewage treatment. However, also in this method, high concentration of orthrin is contained in the digested sludge dewatered filtrate, and this is returned to the water treatment system, so that the load increases, which is one of the causes of deterioration of the secondary treatment water quality. Become.

【0006】また、生物学的リン除去法で原水中から除
去されたリンは、汚泥中に高濃度で蓄積し、嫌気条件下
で水側に再放出されるため、水処理に悪影響を及ぼすこ
とが懸念される。したがって再放出されたリンを効率的
に除去する方法が求められている。
[0006] Further, phosphorus removed from raw water by the biological phosphorus removal method accumulates in sludge at a high concentration and is re-released to the water side under anaerobic conditions, which adversely affects water treatment. Is concerned. Therefore, there is a need for a method for efficiently removing re-released phosphorus.

【0007】[0007]

【発明が解決しようとする課題】従来のリンの除去は、
第二鉄塩や硫酸アルミニウム(ばん土)のような金属塩
及び石灰からなる凝集剤を用いて下水中のリンを凝集さ
せ、これを沈殿除去する凝集沈殿法が最も一般に行われ
ている。しかしながら、この方法では汚泥発生量が多く
なり、しかもそれらは難脱水性であるなどの問題があ
る。
The conventional removal of phosphorus is as follows.
The coagulation sedimentation method of coagulating phosphorus in sewage using a coagulant composed of a metal salt such as ferric salt or aluminum sulfate (salt) and lime, and precipitating and removing this is most commonly performed. However, this method has a problem that the amount of generated sludge is large, and they are difficult to dehydrate.

【0008】そこで本発明は、下水の処理によって発生
する汚泥中のリンを効率よく除去することができ、排水
処理設備の負荷の軽減や二次処理水中へのリンの流出防
止を図ることができる排水処理装置を提供することを目
的としている。
Therefore, the present invention can efficiently remove phosphorus in sludge generated by sewage treatment, reduce the load on wastewater treatment equipment, and prevent phosphorus from flowing into secondary treated water. It aims at providing a wastewater treatment device.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するた
め、本発明の排水処理装置は、リン含有汚泥中の固形物
を沈殿分離する固液分離槽と、該固液分離槽で固形物を
分離した分離液に脱リン剤及びカルシウムイオンを添加
して分離液中のリンと添加したカルシウムとを反応させ
て析出させることにより分離液中からリンを除去する脱
リン槽とを備えていることを特徴とし、また、前記固液
分離槽で分離した固形物と、前記脱リン槽でリンを除去
した脱リン液とを混合して汚泥濃縮設備に送る経路を備
えていることを特徴としている。
In order to achieve the above object, a wastewater treatment apparatus according to the present invention comprises a solid-liquid separation tank for separating and separating solids in phosphorus-containing sludge, and a solid-liquid separation tank for separating solids in the solid-liquid separation tank. A dephosphorization tank that removes phosphorus from the separated liquid by adding a dephosphorizing agent and calcium ions to the separated liquid and reacting and depositing phosphorus in the separated liquid with the added calcium; And a path for mixing the solid separated in the solid-liquid separation tank with the dephosphorized solution from which phosphorus has been removed in the dephosphorization tank and sending it to a sludge concentration facility. .

【0010】[0010]

【発明の実施の形態】図1は本発明の排水処理装置の一
形態例を示す説明図である。この排水処理装置は、リン
含有汚泥中の固形物を沈殿分離する固液分離槽10と、
リンとカルシウムとを反応させて除去する脱リン槽20
と、カルシウム化合物貯留槽30及びpH調整剤貯留槽
31を有するものであって、固液分離槽10には、排水
処理設備の消化槽等から引抜いたリン含有汚泥の流入管
11と、固液分離した上層の分離液を脱リン槽20に供
給する分離液供給管12と、槽底部に沈降した固形物を
引抜く固形物引抜管13とが設けられている。
DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is an explanatory view showing one embodiment of a waste water treatment apparatus according to the present invention. The wastewater treatment apparatus includes a solid-liquid separation tank 10 that precipitates and separates solids in phosphorus-containing sludge,
Dephosphorization tank 20 for reacting and removing phosphorus and calcium
And a calcium compound storage tank 30 and a pH adjusting agent storage tank 31. The solid-liquid separation tank 10 has an inflow pipe 11 for phosphorus-containing sludge drawn from a digestion tank or the like of a wastewater treatment facility, and a solid-liquid separation tank 10. A separation liquid supply pipe 12 for supplying the separated upper layer separation liquid to the dephosphorization tank 20 and a solid substance extraction pipe 13 for extracting solid substances settled at the bottom of the tank are provided.

【0011】前記脱リン槽20は、上部が大径で底面を
漏斗状に形成した有底円筒状のものであって、その内部
には、大径小径2個の円筒体21,22が設けられてい
る。大径円筒体21の内周部上方には、前記分離液供給
管12の流出部が位置しており、さらに、カルシウム化
合物供給管23、pH調整剤供給管24及び脱リン剤供
給管25がそれぞれ設けられている。また、小径円筒体
22の内部には、該円筒体22内に下向流を発生させる
撹拌機26が設けられている。
The dephosphorization tank 20 is a bottomed cylinder having a large diameter at the top and a funnel-shaped bottom, and two large and small diameter cylinders 21 and 22 are provided therein. Have been. The outlet of the separated liquid supply pipe 12 is located above the inner peripheral part of the large-diameter cylindrical body 21, and further, a calcium compound supply pipe 23, a pH adjusting agent supply pipe 24, and a dephosphorizing agent supply pipe 25 are provided. Each is provided. Further, a stirrer 26 for generating a downward flow in the cylindrical body 22 is provided inside the small-diameter cylindrical body 22.

【0012】さらに、脱リン槽20の底部には、リンと
カルシウムとが反応して脱リン剤表面に析出したリン・
カルシウム化合物(リン酸カルシウム、リン酸水素カル
シウム、ヒドロキシアパタイト等)の結晶を排出するた
めの生成物排出部27が設けられ、上部には脱リン液排
出部28が設けられている。また、脱リン槽20の適宜
な位置には、pH計29が設けられており、このpH計
29の測定値に応じてpH調整剤供給管24からpH調
整剤が投入される。
Further, on the bottom of the dephosphorization tank 20, phosphorus and calcium react with each other to precipitate phosphorus on the surface of the dephosphorizing agent.
A product discharge portion 27 for discharging crystals of a calcium compound (calcium phosphate, calcium hydrogen phosphate, hydroxyapatite, etc.) is provided, and a dephosphorization solution discharge portion 28 is provided on the upper portion. Further, a pH meter 29 is provided at an appropriate position of the dephosphorization tank 20, and a pH adjuster is supplied from the pH adjuster supply pipe 24 in accordance with a measured value of the pH meter 29.

【0013】上記大径円筒体21は、脱リン槽上部の大
径部内に設けられており、上端は水面より上方に位置す
るように設置されている。この大径円筒体21の内部に
設置される小径円筒体22は、大径円筒体21の内周部
及び脱リン槽20の下部内周部との間をドラフトチュー
ブ型撹拌部とするものであって、撹拌機26により小径
円筒体22の内周に下向流が、外周に上昇流がそれぞれ
形成されて循環流となる。
The large-diameter cylindrical body 21 is provided in the large-diameter portion above the dephosphorization tank, and the upper end is installed so as to be located above the water surface. The small-diameter cylindrical body 22 installed inside the large-diameter cylindrical body 21 has a draft tube-type stirring section between the inner peripheral part of the large-diameter cylindrical body 21 and the lower inner peripheral part of the dephosphorization tank 20. Then, a downward flow is formed on the inner periphery of the small-diameter cylindrical body 22 by the stirrer 26, and an upward flow is formed on the outer periphery, thereby forming a circulating flow.

【0014】また、大径円筒体21の外周部と、脱リン
槽20上部の大径部の内周部との間は、分離液流入管1
2から流入する分離液量に略相当する液が上昇し、反応
により生成した結晶を、その上昇過程で沈降分離させる
結晶分離部として作用する。この部分は、小結晶も確実
に沈降させるために十分な水面積で形成されている。
A separation liquid inflow pipe 1 is provided between the outer peripheral portion of the large-diameter cylindrical body 21 and the inner peripheral portion of the large-diameter portion above the dephosphorization tank 20.
The liquid substantially corresponding to the amount of the separated liquid flowing in from 2 rises, and acts as a crystal separation section for sedimenting and separating the crystals generated by the reaction in the rising process. This portion is formed with a sufficient water area to surely settle even small crystals.

【0015】脱リン槽20では、分離液流入管12から
流入する分離液と、カルシウム化合物供給管23から供
給されるカルシウム化合物とが小径円筒体22の周囲を
循環する過程で混合され、分離液中のリンと添加された
カルシウムとが反応してリン・カルシウム化合物が生成
し、最初は、種結晶としてあらかじめ投入されたリン酸
カルシウムの結晶やりん鉱石等の脱リン剤の表面に析出
する。さらに、この表面で反応が進んで結晶が次第に成
長し、ある程度の大きさの結晶になると比重差により循
環流から分かれて槽底部に沈降する。
In the dephosphorization tank 20, the separation liquid flowing from the separation liquid inflow pipe 12 and the calcium compound supplied from the calcium compound supply pipe 23 are mixed in the process of circulating around the small-diameter cylindrical body 22, and are separated. The phosphorus contained therein reacts with the added calcium to produce a phosphorus / calcium compound, which is initially deposited on the surface of a phosphorus phosphate or other dephosphorizing agent such as calcium phosphate crystals or phosphate rock previously introduced as seed crystals. Further, the reaction proceeds on this surface, and the crystal grows gradually. When the crystal becomes a certain size, the crystal separates from the circulating flow due to a difference in specific gravity and settles at the bottom of the tank.

【0016】このとき、前段の固液分離槽10で流入汚
泥中の固形物をあらかじめ十分に沈殿分離しておくこと
により、脱リン槽20底部の生成物排出部27から、純
度が高く、肥料として有効に利用できるリン・カルシウ
ム化合物を取出すことができる。
At this time, the solid matter in the inflow sludge is sufficiently settled and separated in advance in the solid-liquid separation tank 10 in the former stage, so that the high purity and fertilizer can be obtained from the product discharge part 27 at the bottom of the dephosphorization tank 20. Phosphorus / calcium compounds that can be effectively used as a sulphate can be obtained.

【0017】また、リン除去した脱リン液は、槽上部の
脱リン液排出部28から抜出され、排水処理設備の適宜
な位置に戻されて再処理される。さらに、固液分離槽1
0の固形物引抜管13から引抜かれた固形物は、汚泥濃
縮設備等に送られて所定の処理が行われる。
The dephosphorized solution from which phosphorus has been removed is withdrawn from the dephosphorized solution discharge section 28 at the top of the tank, returned to an appropriate position in the wastewater treatment facility, and reprocessed. Further, the solid-liquid separation tank 1
The solid extracted from the solid extraction pipe 13 is sent to a sludge concentration facility or the like, where a predetermined process is performed.

【0018】このようにしてリンを除去することによ
り、汚泥中にリンが大量に蓄積されることを防止でき、
二次処理水中にリンが流出することを防止できるととも
に、配管中へのスケールの付着を防止でき、汚泥量が増
加することもなく、排水処理設備の負荷も軽減できる。
By thus removing phosphorus, it is possible to prevent a large amount of phosphorus from being accumulated in sludge,
It is possible to prevent phosphorus from flowing out into the secondary treatment water, to prevent scale from adhering to the piping, to reduce the amount of sludge, and to reduce the load on the wastewater treatment equipment.

【0019】図2は本発明の他の形態例を示す説明図で
ある。本形態例の装置構成は、前記形態例と略同様であ
るから、前記形態例の構成要素と同一の構成要素には同
一の符号を付して詳細な説明は省略する。
FIG. 2 is an explanatory view showing another embodiment of the present invention. Since the device configuration of the present embodiment is substantially the same as that of the above-described embodiment, the same components as those of the above-described embodiment are denoted by the same reference numerals, and detailed description thereof will be omitted.

【0020】この形態例では、固液分離槽10における
固液分離を、砂等の比重の大きなものの分離だけにとど
め、大部分の汚泥は、そのまま脱リン槽20に供給して
脱リン処理を行うようにし、固液分離槽10の固形物引
抜管13から引抜いた固形物と、脱リン槽20の脱リン
液排出部28から抜出された汚泥含有脱リン液は、合流
経路41に合流させて汚泥濃縮設備42に送るようにし
ている。
In this embodiment, the solid-liquid separation in the solid-liquid separation tank 10 is limited only to separation of a substance having a large specific gravity, such as sand, and most of the sludge is directly supplied to the dephosphorization tank 20 for dephosphorization. The solid matter withdrawn from the solid matter extraction pipe 13 of the solid-liquid separation tank 10 and the sludge-containing dephosphorization liquid withdrawn from the dephosphorization liquid discharge unit 28 of the dephosphorization tank 20 merge into the merge path 41. Then, it is sent to the sludge concentration equipment 42.

【0021】このとき、脱リン槽20では、固液分離槽
10から供給された汚泥が結晶と共に槽底部に沈殿する
ことを防止しながら、脱リン水と共に脱リン液排出部2
8から流出させ、かつ、結晶を流出させずに沈降させる
ため、結晶の沈降速度V1と、大径円筒体21外周部の
結晶分離部における上昇流の断面流速V2と、固液分離
槽10における上昇流の断面流速V3との関係を、V1
>V2>V3となるように設定しておくことが好まし
い。
At this time, in the dephosphorization tank 20, the sludge supplied from the solid-liquid separation tank 10 is prevented from settling at the bottom of the tank together with the crystals, and the dephosphorization solution discharge section 2 is used together with the dephosphorization water.
8 and sedimentation without causing the crystal to flow out, the sedimentation velocity V1 of the crystal, the cross-sectional flow velocity V2 of the ascending flow in the crystal separation part on the outer periphery of the large-diameter cylindrical body 21, and the solid-liquid separation tank 10 The relationship between the sectional flow velocity V3 of the upward flow and V1
>V2> V3.

【0022】このように、汚泥濃縮設備42が設けられ
ている排水処理設備の場合は、固液分離槽10におい
て、脱リン槽20で生成した結晶と共に沈殿してしまう
ような比重の大きなものだけを分離するように設定する
ことにより、固液分離槽10の容量を前記形態例に比べ
て大幅に小さくすることができるので、装置の小型化が
図れ、既存の排水処理設備における消化槽と汚泥濃縮設
備42との間の限られた空間内にも容易に設置すること
ができる。
As described above, in the case of the wastewater treatment equipment provided with the sludge concentration equipment 42, only those having a large specific gravity in the solid-liquid separation tank 10 that precipitate together with the crystals generated in the dephosphorization tank 20. By setting so as to separate the wastewater, the capacity of the solid-liquid separation tank 10 can be significantly reduced as compared with the embodiment described above, so that the size of the apparatus can be reduced and the digestion tank and sludge in the existing wastewater treatment equipment can be reduced. It can be easily installed even in a limited space between the concentration equipment 42.

【0023】[0023]

【発明の効果】以上説明したように、本発明の排水処理
装置によれば、消化汚泥等に含まれるリンを効率よく除
去することができるので、二次処理水中にリンが流出す
ることを確実に防止できるとともに、水処理設備の負荷
も軽減させることができ、安定した水処理運転を行うこ
とができる。
As described above, according to the wastewater treatment apparatus of the present invention, phosphorus contained in digested sludge and the like can be efficiently removed, so that it is ensured that phosphorus flows out into the secondary treated water. And the load on the water treatment equipment can be reduced, and a stable water treatment operation can be performed.

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

【図1】 本発明の排水処理装置の一形態例を示す説明
図である。
FIG. 1 is an explanatory view showing one embodiment of a wastewater treatment apparatus according to the present invention.

【図2】 本発明の排水処理装置の他の形態例を示す説
明図である。
FIG. 2 is an explanatory view showing another embodiment of the wastewater treatment device of the present invention.

【符号の説明】[Explanation of symbols]

10…固液分離槽、11…流入管、12…分離液供給
管、13…固形物引抜管、20…脱リン槽、21…大径
円筒体、22…小径円筒体、23…カルシウム化合物供
給管、24…pH調整剤供給管、25…脱リン剤供給
管、26…撹拌機、27…生成物排出部、28…脱リン
液排出部、29…pH計、30…カルシウム化合物貯留
槽、31…pH調整剤貯留槽、41…合流経路、42…
汚泥濃縮設備
DESCRIPTION OF SYMBOLS 10 ... Solid-liquid separation tank, 11 ... Inflow pipe, 12 ... Separation liquid supply pipe, 13 ... Solid substance extraction pipe, 20 ... Dephosphorization tank, 21 ... Large diameter cylinder, 22 ... Small diameter cylinder, 23 ... Calcium compound supply Pipe, 24: pH adjuster supply pipe, 25: dephosphorizer supply pipe, 26: stirrer, 27: product discharge section, 28: dephosphorization liquid discharge section, 29: pH meter, 30: calcium compound storage tank, 31: pH adjusting agent storage tank, 41: Merging path, 42:
Sludge thickening equipment

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 リン含有汚泥中の固形物を沈殿分離する
固液分離槽と、該固液分離槽で固形物を分離した分離液
に脱リン剤及びカルシウムイオンを添加して分離液中の
リンと添加したカルシウムとを反応させて析出させるこ
とにより分離液中からリンを除去する脱リン槽とを備え
ていることを特徴とする排水処理装置。
1. A solid-liquid separation tank for precipitating and separating solids in a phosphorus-containing sludge, and a dephosphorizing agent and calcium ions are added to the separated liquid from which solids are separated in the solid-liquid separation tank, and A wastewater treatment apparatus comprising: a phosphorus removal tank that removes phosphorus from a separated solution by reacting phosphorus and added calcium to cause precipitation.
【請求項2】 前記固液分離槽で分離した固形物と、前
記脱リン槽でリンを除去した脱リン液とを混合して汚泥
濃縮設備に送る経路を備えていることを特徴とする請求
項1記載の排水処理装置。
2. A path for mixing a solid separated in the solid-liquid separation tank with a dephosphorized solution from which phosphorus has been removed in the dephosphorization tank and sending the mixture to a sludge concentration facility. Item 2. A wastewater treatment device according to Item 1.
JP22015399A 1999-08-03 1999-08-03 Wastewater treatment equipment Expired - Fee Related JP4439040B2 (en)

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Application Number Priority Date Filing Date Title
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JP2001038370A true JP2001038370A (en) 2001-02-13
JP4439040B2 JP4439040B2 (en) 2010-03-24

Family

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Family Applications (1)

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Country Link
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007117874A (en) * 2005-10-27 2007-05-17 Ebara Corp Method and apparatus for treating wastewater containing component to be crystallized
JP2010042365A (en) * 2008-08-13 2010-02-25 Yukio Yanagisawa Dephosphorizing material, dephosphorizing apparatus and dephosphorization by-product
JP2013141622A (en) * 2012-01-06 2013-07-22 Japan Organo Co Ltd Crystallization reactor
WO2014207837A1 (en) * 2013-06-26 2014-12-31 オルガノ株式会社 Crystallization reactor
JP2016087541A (en) * 2014-11-04 2016-05-23 水ing株式会社 Phosphorus recovery and scale prevention method in organic waste water treatment and apparatus

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007117874A (en) * 2005-10-27 2007-05-17 Ebara Corp Method and apparatus for treating wastewater containing component to be crystallized
JP4503523B2 (en) * 2005-10-27 2010-07-14 荏原エンジニアリングサービス株式会社 A method and apparatus for treating wastewater containing a crystallization target component.
JP2010042365A (en) * 2008-08-13 2010-02-25 Yukio Yanagisawa Dephosphorizing material, dephosphorizing apparatus and dephosphorization by-product
JP2013141622A (en) * 2012-01-06 2013-07-22 Japan Organo Co Ltd Crystallization reactor
WO2014207837A1 (en) * 2013-06-26 2014-12-31 オルガノ株式会社 Crystallization reactor
KR101793809B1 (en) * 2013-06-26 2017-11-03 오르가노 코포레이션 Crystallization reactor
JP2016087541A (en) * 2014-11-04 2016-05-23 水ing株式会社 Phosphorus recovery and scale prevention method in organic waste water treatment and apparatus

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