JPH0810793A - Nitrification and denitrification equipment - Google Patents

Nitrification and denitrification equipment

Info

Publication number
JPH0810793A
JPH0810793A JP6152272A JP15227294A JPH0810793A JP H0810793 A JPH0810793 A JP H0810793A JP 6152272 A JP6152272 A JP 6152272A JP 15227294 A JP15227294 A JP 15227294A JP H0810793 A JPH0810793 A JP H0810793A
Authority
JP
Japan
Prior art keywords
nitrification
denitrification
tank
vessels
air
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
JP6152272A
Other languages
Japanese (ja)
Other versions
JP3223945B2 (en
Inventor
Taiji Funakoshi
越 泰 司 船
Masayuki Kojima
島 正 行 小
Hitoshi Kawajiri
尻 斉 川
Teruhiro Kitazawa
沢 照 啓 北
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.)
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Technologies 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 Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Technologies Ltd
Priority to JP15227294A priority Critical patent/JP3223945B2/en
Publication of JPH0810793A publication Critical patent/JPH0810793A/en
Application granted granted Critical
Publication of JP3223945B2 publication Critical patent/JP3223945B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Activated Sludge Processes (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PURPOSE:To efficiently execute nitrification and denitrification treatments by respectively forming denitrification vessels which are partitioned to two vessels, upper and lower, by partition walls and have raw water inflow ports in the lower story and nitrification vessels which have outflow water paths for treated water in the upper story and circulate liquids in order of the outflow water paths, pipings and the inflow water paths between the nitrification vessels and the denitrification vessels. CONSTITUTION:The nitrification and denitrification equipments 14 of a biological reaction plate 10 adjacently provided with an aeration tank 12 and plural sets of the nitrification and denitrification equipment 14 are composed by segmenting the main bodies to the nitrification vessels 28 and the denitrification vessels 20 by the partition walls 26. The outflow water paths 38 disposed in the nitrification vessels 28 and the inside of the denitrification vessels 20 are communicated by communicating pipes 52. The inside of the denitrification vessels 20 and the inflow water paths 54 disposed in the nitrification vessels 28 are communicated by communicating pipes 55. The liquid is circulated between both vessels 28 and 20 by the air lift effect from air diffusers 3 of the nitrification vessels 28. As a result, the air 66 from the air diffusers 33 or the liquid of the nitrification vessels 28 having the high concn. of dissolved oxygen are prevented from short passing into the denitrification vessels 20, by which the increase of dissolved oxygen in the denitrification vessels 20 is prevented.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の利用分野】本発明は廃水の生物処理装置に係
り、特に硝化槽と脱窒槽を備え、硝化液の一部を脱窒槽
に循環する硝化・脱窒装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a biological treatment apparatus for wastewater, and more particularly to a nitrification / denitrification apparatus that includes a nitrification tank and a denitrification tank and circulates a part of the nitrification solution into the denitrification tank.

【0002】[0002]

【従来の技術】この種の硝化・脱窒装置は、脱窒槽を通
って硝化槽に流入した原水は、硝化槽において好気性状
態で硝化処理され、その硝化液の一部は、脱窒槽に循環
されて嫌気性状態で脱窒処理される。この脱窒処理によ
り発生した窒素ガスが脱窒槽の液面から外気に放出さ
れ、これにより廃水中のアンモニア態窒素が除去され
る。そして、従来の硝化・脱窒装置の場合、硝化槽で硝
化処理された硝化液の一定量を循環ポンプにより脱窒槽
に循環していた。しかし、このポンプによる循環方式は
ポンプ動力を必要とし、特に硝化槽から脱窒槽への循環
比が増大した場合には、装置の動力費が大幅に大きくな
るという欠点がある。
2. Description of the Related Art In this type of nitrification / denitrification apparatus, raw water flowing into the nitrification tank through the denitrification tank is nitrified in the nitrification tank in an aerobic state, and a part of the nitrification liquid is transferred to the denitrification tank. It is circulated and denitrified in an anaerobic state. Nitrogen gas generated by this denitrification process is released from the liquid surface of the denitrification tank to the outside air, whereby ammonia nitrogen in the wastewater is removed. In the case of the conventional nitrification / denitrification apparatus, a fixed amount of nitrification solution nitrified in the nitrification tank was circulated to the denitrification tank by a circulation pump. However, the circulation system using this pump requires pump power, and there is a drawback in that the power cost of the apparatus increases significantly when the circulation ratio from the nitrification tank to the denitrification tank increases.

【0003】このことから、循環ポンプを必要としない
で硝化液を脱窒槽に循環する方式の硝化・脱窒装置が採
用されている。この硝化・脱窒装置は、直方体状の装置
本体の長手方向(硝化槽と脱窒槽の並び方向)の略中央
を仕切壁で仕切って、一方を脱窒槽とすると共に他方を
硝化槽とする。そして、硝化槽内を好気性状態にするた
めの散気装置又は専用の散気装置によるエアリフト作用
により硝化槽の硝化液を、前記長手方向に配設された硝
化槽と脱窒槽とを連通する循環水路に溢流させて硝化槽
から脱窒槽に硝化液を循環する。
For this reason, a nitrification / denitrification system of the type in which the nitrification liquid is circulated through the denitrification tank without the need for a circulation pump has been adopted. In this nitrification / denitrification apparatus, a partition wall is provided to partition the substantially central portion of the rectangular parallelepiped apparatus main body in the longitudinal direction (the direction in which the nitrification tank and the denitrification tank are arranged), and one of them serves as a denitrification tank and the other serves as a nitrification tank. Then, the nitrification liquid in the nitrification tank is communicated with the nitrification tank and the denitrification tank arranged in the longitudinal direction by an air lift function by an air diffuser or a dedicated air diffuser for making the inside of the nitrification tank aerobic. The nitrification liquid is circulated from the nitrification tank to the denitrification tank by overflowing the circulation channel.

【0004】しかしながら、エアリフト作用を利用した
循環方式の硝化・脱窒装置の場合、ポンプによる循環方
式に比べて省エネになるメリットがあるものの、硝化・
脱窒装置の長手方向は100メータ程度と長いので、前
記循環水路が極めて長くなるという欠点がある。また、
循環水路が長くなることにより、消化液の循環量の制御
がしにくくなるという欠点がある。また、このように、
硝化槽と脱窒槽とを同一平面上に並べる横型の硝化・脱
窒装置の場合、硝化・脱窒装置を設置するために大きな
スペース(敷地面積)を要するという欠点がある。
However, in the case of the circulation type nitrification / denitrification apparatus utilizing the air lift action, although there is a merit of energy saving as compared with the circulation type using a pump,
Since the longitudinal direction of the denitrification device is as long as about 100 meters, there is a drawback that the circulating water channel becomes extremely long. Also,
There is a drawback in that it becomes difficult to control the circulation amount of digestive juice due to the long circulation channel. Also, like this,
In the case of a horizontal nitrification / denitrification device in which the nitrification tank and the denitrification tank are arranged on the same plane, there is a drawback that a large space (site area) is required to install the nitrification / denitrification apparatus.

【0005】このような背景から、エアリフト作用を利
用し、且つ、大きなスペースを要しない硝化・脱窒装置
として、装置本体を仕切壁で上下2槽に区画した縦型の
硝化・脱窒装置が提案されている。この種の硝化・脱窒
装置としては、本願出願人が既に出願したもので、特開
昭60─193593号公報に開示された廃水の生物処
理装置がある。この生物処理装置は、装置本体を仕切壁
で上下2槽(上階が硝化槽、下階が脱窒槽)に区画する
と共に、仕切壁の開放部において上下2槽を連通させ
る。そして、硝化槽底部に設けられた散気装置からのエ
アによるエアリフト作用により、硝化槽と脱窒槽との間
で前記開放部を介して循環するようにした。また、同様
の硝化・脱窒装置としては、実公昭58─33840号
公報に開示された廃水の脱窒素槽がある。この装置は、
装置本体を隔壁により上下2槽(上階が硝化槽、下階が
脱窒槽)に区画すると共に、該2槽を隔壁に形成した連
通流路(前記開放部に相当)によって連結し、且つ隔壁
に開口を介して脱窒槽内に垂直方向に配置されたエアリ
フト部で連結し、このエアリフト部内にエアを散気す
る。そして、エアリフト部内に散気されるエアリフト作
用により、上下2槽の液が前記連通流路及びエアリフト
部を介して循環するようにした。
From such a background, as a nitrification / denitrification apparatus utilizing the air lift action and requiring no large space, a vertical type nitrification / denitrification apparatus in which the apparatus main body is divided into upper and lower two tanks by a partition wall is proposed. Proposed. As this type of nitrification / denitrification device, there is a wastewater biological treatment device which has been filed by the applicant of the present application and is disclosed in JP-A-60-193593. In this biological treatment apparatus, the main body of the apparatus is partitioned by a partition wall into two upper and lower tanks (a nitrification tank on the upper floor and a denitrification tank on the lower floor), and the upper and lower two tanks communicate with each other at the opening of the partition wall. Then, the air is lifted by air from an air diffuser provided at the bottom of the nitrification tank to circulate the nitrification tank and the denitrification tank through the opening. Further, as a similar nitrification / denitrification device, there is a waste water denitrification tank disclosed in Japanese Utility Model Publication No. 58-33840. This device
The apparatus main body is divided into two upper and lower tanks (nitrification tank on the upper floor and denitrification tank on the lower floor) by partition walls, and the two tanks are connected by a communication channel (corresponding to the opening) formed in the partition walls, and the partition walls The air is connected to the air lift section vertically arranged in the denitrification tank through the opening, and air is diffused in the air lift section. Then, the liquid in the upper and lower two tanks is circulated through the communication flow path and the air lift portion by the air lift action diffused in the air lift portion.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、特開昭
60─193593号公報及び実公昭58─33840
号公報に開示された従来の縦型の硝化・脱窒装置は、以
下の欠点がある。 好気性状態を必要とする硝化槽の液と、嫌気性状態を
必要とする脱窒槽の液とが、仕切壁(又は隔壁)の開放
部(又は連通流路)により直接的に連通している。従っ
て、開放部に発生している硝化槽から脱窒槽への流れに
乗って、散気装置からのエア、或いは溶存酸素の高い状
態の硝化槽の液が脱窒槽に混入し易く、脱窒槽の液の溶
存酸素が高くなる。これにより、脱窒槽内が嫌気状態が
良好に維持できないので、脱窒反応が阻害されるという
欠点がある。
However, JP-A-60-193593 and JP-B-58-33840 are used.
The conventional vertical nitrification / denitrification apparatus disclosed in Japanese Patent Publication has the following drawbacks. The liquid in the nitrification tank that requires aerobic condition and the liquid in the denitrification tank that requires anaerobic condition are in direct communication with each other through the open part (or communication passage) of the partition wall (or partition wall). . Therefore, riding on the flow from the nitrification tank to the denitrification tank generated in the open part, the air from the air diffuser or the liquid of the nitrification tank in the state of high dissolved oxygen easily mixes into the denitrification tank, The dissolved oxygen in the liquid becomes high. As a result, the inside of the denitrification tank cannot maintain a good anaerobic condition, which has a drawback that the denitrification reaction is hindered.

【0007】また、脱窒槽の上階に硝化槽があるの
で、脱窒槽で脱窒反応により発生するメタンガスや窒素
ガス等の消化ガスが、硝化槽内を経由してから外気に達
する。従って、前記した横型の硝化・脱窒装置に比べて
大気に放出されにくいという欠点があると共に、硝化槽
内を経由するので硝化反応に悪影響を与えるという欠点
がある。
Further, since the nitrification tank is located on the upper floor of the denitrification tank, digestive gases such as methane gas and nitrogen gas generated by the denitrification reaction in the denitrification tank reach the outside air after passing through the nitrification tank. Therefore, compared with the horizontal nitrification / denitrification apparatus described above, it has a drawback that it is less likely to be released to the atmosphere, and has a drawback that it adversely affects the nitrification reaction because it passes through the nitrification tank.

【0008】また、硝化槽の液を脱窒槽に循環させる
為には、硝化槽と脱窒槽との間で旋回流を発生させなく
てはならず、硝化槽全面への全面散気を行うことができ
ない。これにより、硝化槽内において、散気量の充分な
エリアと不足するエリアが発生し易いので、硝化槽内で
の消化反応が不均一になるという欠点がある。上記した
ように、従来の横型の硝化・脱窒装置は、大きな設置ス
ペース、長い循環水路、循環量の制御のしずらさの点で
欠点があり、従来の縦型の硝化・脱窒装置は、硝化槽の
良好な好気性条件及び脱窒槽の良好な嫌気性条件が形成
できにくく、硝化・脱窒処理を効率的に行うことができ
ないと共に、脱窒槽で発生する消化ガスが外気に放出さ
れにくいという欠点がある。従って、何れの硝化・脱窒
装置ともに満足できるものではなかった。
Further, in order to circulate the liquid in the nitrification tank to the denitrification tank, a swirl flow must be generated between the nitrification tank and the denitrification tank, and the entire surface of the nitrification tank is diffused. I can't. As a result, in the nitrification tank, an area with a sufficient amount of air diffused and an area with insufficient air diffusion are likely to occur, and there is a drawback that the digestion reaction in the nitrification tank becomes uneven. As described above, the conventional horizontal nitrification / denitrification device has drawbacks in that it has a large installation space, a long circulating water channel, and difficulty in controlling the circulation amount. It is difficult to form good aerobic conditions in the nitrification tank and good anaerobic conditions in the denitrification tank, so that nitrification and denitrification treatment cannot be performed efficiently, and digestive gas generated in the denitrification tank is not easily released to the outside air. There is a drawback that. Therefore, none of the nitrification / denitrification equipment was satisfactory.

【0009】本発明はこのような事情に鑑みてなされた
もので、従来の硝化・脱窒装置の欠点を解消し、硝化・
脱窒処理を効率的に行うことができると共に、循環量の
制御がし易く、しかも装置の省エネ、コンパクト化を図
ることのできる硝化・脱窒装置を提供することを目的と
する。
The present invention has been made in view of the above circumstances, and eliminates the drawbacks of the conventional nitrification / denitrification apparatus, and
An object of the present invention is to provide a nitrification / denitrification device that can efficiently perform denitrification processing, can easily control the circulation amount, and can save energy and make the device compact.

【0010】[0010]

【課題を解決する為の手段】本発明は、前記目的を達成
する為に、仕切壁により上下2槽に仕切って、原水流入
口を有する脱窒槽を下階に形成すると共に、処理水の流
出水路を有する硝化槽を上階に形成した装置本体と、前
記硝化槽内に添加され、硝化菌を担持した多数の担体
と、前記流出水路に一方の開口が連通されると共に、前
記脱窒槽内に他方の開口が形成される第1の連通管と、
前記脱窒槽内に一方の開口が形成されると共に、前記硝
化槽内又は硝化槽に近接して設けられ硝化槽内に通じる
流入水路に他方の開口が連通される第2の連通管と、前
記硝化槽の底部に設けられ、硝化槽内にエアを散気する
散気装置と、から成り、前記硝化槽と前記脱窒槽との間
で、前記流出水路、前記第1の配管、前記第2の配管、
前記流入水路の順路で液を循環させることを特徴とす
る。
In order to achieve the above-mentioned object, the present invention forms a denitrification tank having a raw water inlet on the lower floor by dividing the tank into upper and lower two tanks by a partition wall, and discharging treated water. An apparatus main body having a nitrification tank having a water channel formed on the upper floor, a large number of carriers added in the nitrification tank and carrying nitrifying bacteria, and one opening communicating with the outflow water channel, and in the denitrification tank A first communication pipe having the other opening formed therein,
A second communication pipe having one opening formed in the denitrification tank, the other opening being in communication with an inflow water channel provided in the nitrification tank or in the vicinity of the nitrification tank and communicating with the nitrification tank; An air diffuser provided at the bottom of the nitrification tank for diffusing air into the nitrification tank, and between the nitrification tank and the denitrification tank, the outflow water channel, the first pipe, and the second Plumbing,
It is characterized in that the liquid is circulated in the normal path of the inflow water channel.

【0011】[0011]

【作用】本発明の硝化・脱窒装置は、下階に脱窒槽を、
上階に硝化槽を設け敷地面積を小さくできる上下2槽構
造にすると共に、従来の上下2槽構造の欠点を以下の構
造にすることにより解消した。即ち、本発明の硝化・脱
窒装置によれば、装置本体は仕切壁で硝化槽と脱窒槽と
に完全に仕切る一方、硝化槽に設けた処理水の流出水路
と脱窒槽内とを第1の連通管で連通すると共に、脱窒槽
内と、硝化槽内又は硝化槽に近接して設けられ硝化槽内
に連通する流入水路とを第2の連通管で連通する。そし
て、硝化槽と脱窒槽との間で、流出水路、第1の配管、
第2の配管、流入水路の順路で液を循環させるようにし
た。即ち、従来の縦型の硝化・脱窒装置のように仕切壁
に形成した開口部により硝化槽と脱窒槽とが直接的に連
通しない。これにより、硝化槽に設けられた散気装置か
らのエア、或いは溶存酸素の高い状態の硝化槽の液が脱
窒槽内に混入しないので、脱窒槽内の液の溶存酸素が高
くなるのを防止できる。更には、硝化槽の液が第1の連
通管内を流れて脱窒槽に下降する間に、液中の気泡が上
昇して抜けるので、脱窒槽の嫌気状態をより良好に維持
できる。従って、脱窒槽内の嫌気状態が良好に維持され
るので、脱窒反応を効率良く行うことができる。また、
流出水路近傍に、流出水路に流れ込む液の泡を消す消泡
装置を設けると、更に脱窒槽の嫌気状態を一層良好に維
持できる。
[Function] The nitrification / denitrification apparatus of the present invention has a denitrification tank on the lower floor,
The nitrification tank was installed on the upper floor, and the upper and lower two tank structures that can reduce the site area were constructed, and the drawbacks of the conventional upper and lower two tank structures were solved by the following structures. That is, according to the nitrification / denitrification apparatus of the present invention, the apparatus main body is completely partitioned by the partition wall into the nitrification tank and the denitrification tank, while the outflow channel of the treated water and the inside of the denitrification tank provided in the nitrification tank are The second communication pipe communicates with the inside of the denitrification tank and an inflow water channel provided in the nitrification tank or in the vicinity of the nitrification tank and communicating with the nitrification tank. Then, between the nitrification tank and the denitrification tank, an outflow water channel, a first pipe,
The liquid was circulated through the second pipe and the inflow water channel. That is, unlike the conventional vertical nitrification / denitrification apparatus, the nitrification tank and the denitrification tank do not directly communicate with each other due to the opening formed in the partition wall. As a result, the air from the air diffuser installed in the nitrification tank or the liquid in the nitrification tank in a state of high dissolved oxygen does not mix into the denitrification tank, preventing the dissolved oxygen in the liquid in the denitrification tank from increasing. it can. Furthermore, while the liquid in the nitrification tank flows through the first communication pipe and descends into the denitrification tank, air bubbles in the liquid rise and escape, so that the anaerobic state of the denitrification tank can be better maintained. Therefore, since the anaerobic state in the denitrification tank is maintained well, the denitrification reaction can be efficiently performed. Also,
By providing a defoaming device for eliminating bubbles of the liquid flowing into the outflow water channel near the outflow water channel, the anaerobic state of the denitrification tank can be further maintained.

【0012】また、硝化槽と脱窒槽との間の液の循環を
上記の如く構成したので、従来の仕切壁に開放部を形成
して循環させる場合のように、硝化槽と脱窒槽との間で
旋回流を発生させる必要がない。これにより、硝化槽内
全面に全面散気させることができる。従って、硝化槽内
のエアレーションに偏りが発生することがなく、硝化槽
内が良好な好気状態に維持されるので、硝化反応を効率
良く行うことができる。また、硝化槽内に硝化菌を担持
した多数の担体を添加したので、硝化反応が促進され
る。
Further, since the circulation of the liquid between the nitrification tank and the denitrification tank is configured as described above, the nitrification tank and the denitrification tank are separated from each other as in the case of forming an open portion in the conventional partition wall for circulation. There is no need to generate swirling flow between them. Thereby, the entire surface of the nitrification tank can be diffused. Therefore, the aeration in the nitrification tank is not biased, and the inside of the nitrification tank is maintained in a favorable aerobic state, so that the nitrification reaction can be efficiently performed. In addition, since many carriers carrying nitrifying bacteria are added to the nitrification tank, the nitrification reaction is promoted.

【0013】また、液の循環動力として散気装置からの
エアによるエアリフト効果を利用するようにしたので、
ポンプ動力を使用しなくてよいため省エネになる。この
時、第2の連通管内にエアリフト作用を発生させる散気
管、或いは第2の連通管内に上向流を発生させるポンプ
を設けると、循環をよりスムーズに行うことができる。
また、流入水路に循環する液の循環量を制御する制御手
段を設けたので、原水の性状、水温等の条件に応じて液
の循環量を容易に制御できる。
Further, since the air lift effect by the air from the air diffuser is used as the power for circulating the liquid,
It saves energy because it does not need to use pump power. At this time, circulation can be performed more smoothly by providing an air diffuser for generating an air lift action in the second communication pipe or a pump for generating an upward flow in the second communication pipe.
Further, since the control means for controlling the circulation amount of the liquid circulating in the inflow water channel is provided, the circulation amount of the liquid can be easily controlled according to the conditions such as the property of the raw water and the water temperature.

【0014】また、脱窒槽には攪拌装置が設けられると
共に、前記仕切壁の攪拌装置上方位置に形成した開口か
ら硝化槽を通って外気に通じるダクトを設けるようにし
た。これにより、脱窒槽で発生するメタンガスや窒素ガ
ス等の消化ガスを硝化槽を通らずに大気に放出できるの
で、脱窒槽での硝化反応を阻害することがないと共に、
ダクトは攪拌装置の修理等における搬出路として使用す
ることができる。また、前記仕切壁の脱窒槽側の面を、
前記ダクトの開口を頂点とした傾斜を形成すると、前記
消化ガスがダクトの入口に集まり易くなるので、より速
やかに大気に放出させることができる。
Further, the denitrification tank is provided with a stirrer, and a duct is provided through which an opening formed in the partition wall above the stirrer passes through the nitrification tank and communicates with the outside air. As a result, digestive gases such as methane gas and nitrogen gas generated in the denitrification tank can be released to the atmosphere without passing through the nitrification tank, so that the nitrification reaction in the denitrification tank is not hindered,
The duct can be used as a carry-out path for repairing the stirring device. In addition, the surface of the partition wall on the denitrification tank side,
When the slope having the opening of the duct as the apex is formed, the digestive gas is likely to collect at the inlet of the duct, so that it can be released to the atmosphere more quickly.

【0015】[0015]

【実施例】以下添付図面に従って本発明に係る硝化・脱
窒装置の好ましい実施例について詳説する。図1は、嫌
気槽と本発明の硝化・脱窒装置とを組み合わせて、生物
学的にリン成分・窒素成分の同時除去を行う生物反応装
置の内部構造を示す断面図である。図2は本発明の硝化
・脱窒装置を上側(硝化槽側)から見た平面図、図3は
図2のA−A線に沿った縦断面図、図4は図2のB−B
線に沿った断面図である。
The preferred embodiments of the nitrification / denitrification apparatus according to the present invention will be described in detail below with reference to the accompanying drawings. FIG. 1 is a cross-sectional view showing the internal structure of a bioreactor for biologically removing phosphorus and nitrogen simultaneously by combining an anaerobic tank and the nitrification / denitrification apparatus of the present invention. 2 is a plan view of the nitrification / denitrification apparatus of the present invention seen from the upper side (nitrification tank side), FIG. 3 is a vertical sectional view taken along line AA of FIG. 2, and FIG. 4 is BB of FIG.
It is sectional drawing along the line.

【0016】図1に示すように、生物反応装置10は、
嫌気槽12と、複数の本発明の硝化・脱窒装置14、1
4とが隣接して設けられる。そして、嫌気槽12に流入
した原水16は、複数の原水配管18、18によりそれ
ぞれの硝化・脱窒装置14の後記する脱窒槽20に分配
供給される。また、嫌気槽12には大形の水中攪拌機2
2が設けられ、分子状酸素も結合型酸素もない絶対嫌気
状態が形成される。また、嫌気槽に流入する原水流入量
は原水流量調節装置17により調節されると共に、嫌気
槽12から各硝化・脱窒装置14に供給される原水供給
量は、供給流量調節装置24により調節される。
As shown in FIG. 1, the bioreactor 10 comprises:
Anaerobic tank 12 and a plurality of nitrification / denitrification devices 14, 1 of the present invention
And 4 are provided adjacent to each other. Then, the raw water 16 that has flowed into the anaerobic tank 12 is distributed and supplied to the denitrification tank 20 to be described later of each nitrification / denitrification device 14 through a plurality of raw water pipes 18, 18. In addition, the anaerobic tank 12 has a large underwater agitator 2
2 is provided and an absolute anaerobic state is formed with neither molecular oxygen nor bound oxygen. Further, the raw water inflow amount flowing into the anaerobic tank is adjusted by the raw water flow rate adjusting device 17, and the raw water supply amount supplied from the anaerobic tank 12 to each nitrification / denitrification device 14 is adjusted by the supply flow rate adjusting device 24. It

【0017】次に、本発明の硝化・脱窒装置14につい
て説明すると、図1に示すように、直方体状の硝化・脱
窒装置本体14は、仕切壁26により上下2槽に仕切ら
れ、下階に脱窒槽20が形成され、上階に硝化槽28が
形成される。また、脱窒槽20及び硝化槽28には活性
汚泥が添加されると共に、硝化槽28には活性汚泥とは
別に硝化菌を固定化、例えば包括固定した多数の担体3
0が添加される。また、脱窒槽20の底部には水中攪拌
機32が設けられ、この水中攪拌機32で脱窒槽24内
の液ををゆっくり攪拌することにより原水中のエアを脱
気し嫌気状態を形成する。
Next, the nitrification / denitrification apparatus 14 of the present invention will be described. As shown in FIG. 1, the rectangular parallelepiped nitrification / denitrification apparatus main body 14 is partitioned by a partition wall 26 into upper and lower two tanks, and The denitrification tank 20 is formed on the floor, and the nitrification tank 28 is formed on the upper floor. In addition, activated sludge is added to the denitrification tank 20 and the nitrification tank 28, and nitrifying bacteria are immobilized in the nitrification tank 28 separately from the activated sludge, for example, a large number of carriers 3 are entrapped and immobilized.
0 is added. Further, an underwater stirrer 32 is provided at the bottom of the denitrification tank 20, and by slowly stirring the liquid in the denitrification tank 24 with this underwater stirrer 32, the air in the raw water is deaerated to form an anaerobic state.

【0018】一方、硝化槽28内の底面全体には、エア
を噴出する散気装置33の多数の吹出口34、34…が
形成される。そして、散気装置33は高圧エア配管(図
示せず)を介してコンプレッサ(図示せず)に接続され
る。これにより、吹出口34から硝化槽28内の液にエ
アが全面散気され、硝化槽28内に好気性状態を形成し
て原水16中のアンモニア態窒素を硝化処理すると共
に、この全面散気によるエアのエアリフト作用により、
硝化槽28内の水位が高くなる。
On the other hand, a large number of air outlets 34, 34 ... Of an air diffuser 33 for ejecting air are formed on the entire bottom surface in the nitrification tank 28. The air diffuser 33 is connected to a compressor (not shown) via a high pressure air pipe (not shown). As a result, air is diffused over the entire surface of the liquid in the nitrification tank 28 from the air outlet 34, an aerobic state is formed in the nitrification tank 28 to nitrify the ammonia nitrogen in the raw water 16, and the entire surface is diffused. By the air lift action of air by
The water level in the nitrification tank 28 becomes high.

【0019】また、図1〜図4に示すように、硝化槽2
8の長手方向の一方側壁面に沿って、処理水36が装置
外に流出する流出水路38が設けられる。この流出水路
38の硝化槽28側の側面は、前記担体30を分離する
分離スクリーン40で形成されると共に、分離スクリー
ン40の上端には担体流出防止板42が配設される。ま
た、この分離スクリーン40は硝化槽28の底部側に傾
斜して設けられていると共に、分離スクリーン40下方
の硝化槽28内には、分離スクリーン40の洗浄用エア
ノズル44(図3、図4参照)が設けられる。これによ
り、洗浄用エアノズル44からの気泡や、前記担体30
が分離スクリーン40面に衝突することにより分離スク
リーン40が目詰まりしないようにする。また、分離ス
クリーン40上方の硝化槽28外には、分離スクリーン
40近傍の液面に散水する消泡装置46が設けられる。
これにより、散気装置33から吹き出されて硝化槽28
の液面、特に分離スクリーン40近傍に溜まり易い泡を
消泡するので、分離スクリーン40近傍に担体が堆積す
るのを防止すると共に、分離スクリーン40を通過して
流出水路38に泡が流れ込むのを防止することができ
る。
Further, as shown in FIGS. 1 to 4, the nitrification tank 2
An outflow water channel 38 through which the treated water 36 flows out of the apparatus is provided along one longitudinal side wall surface of the device 8. A side surface of the outflow water channel 38 on the side of the nitrification tank 28 is formed with a separation screen 40 for separating the carrier 30, and a carrier outflow prevention plate 42 is arranged at an upper end of the separation screen 40. Further, the separation screen 40 is inclinedly provided on the bottom side of the nitrification tank 28, and in the nitrification tank 28 below the separation screen 40, a cleaning air nozzle 44 of the separation screen 40 (see FIGS. 3 and 4). ) Is provided. Thereby, air bubbles from the cleaning air nozzle 44 and the carrier 30
Prevents the separation screen 40 from being clogged by the collision of the separation screen 40 with the surface of the separation screen 40. Further, outside the nitrification tank 28 above the separation screen 40, a defoaming device 46 that sprays water on the liquid surface near the separation screen 40 is provided.
Accordingly, the nitrification tank 28 is blown out from the air diffuser 33.
Since the bubbles that tend to collect on the liquid surface of the separator, especially near the separation screen 40 are extinguished, the carriers are prevented from accumulating in the vicinity of the separation screen 40, and the bubbles are prevented from flowing through the separation screen 40 into the outflow water channel 38. Can be prevented.

【0020】また、前記流出水路38内には、流出水路
38に沿って流出トラフ48が設けられ、図示しない沈
澱装置に接続されると共に、流出トラフ48の長手方向
中央部に溢流口50(図1、図2参照)が形成される。
また、複数の第1の連通管52、52が仕切壁26を貫
通して縦方向に配設されると共に、その一方端は流出水
路38の底部に連通され、他方端は脱窒槽20内の底部
に開口される。一方、硝化槽28の長手方向の他方側壁
面に沿って、脱窒槽20からの液が流入する流入水路5
4が設けられる。そして、複数の第2の連通管55が仕
切壁26を貫通して縦方向に配設されると共に、その一
方端は流入水路54の底部に連通され、他方端は脱窒槽
20内の上部に開口される(図3参照)。また、流入水
路54の所定位置から硝化槽28の底部近傍まで配管5
6が延設されると共に、延設された配管56の先端は散
気装置33からのエアが侵入しないように横向き或いは
上向きに形成される。これにより、装置本体は仕切壁2
6で硝化槽28と脱窒槽20とに完全に仕切られる一
方、流出水路38、第1の連通管52、第2の連通管5
5、流入水路54、配管56により硝化槽28と脱窒槽
20との間で液を循環させる循環路が形成される。ま
た、流入水路54には循環量制御ゲート57が設けら
れ、これにより、原水の性状や水温等の条件に応じて前
記循環路を流れる循環流量を調節することができる。ま
た、流入水路54の液面上方には、流入水路54の液面
に散水する消泡装置59が設けられる(図3参照)。
In addition, an outflow trough 48 is provided in the outflow water channel 38 along the outflow water channel 38 and is connected to a precipitation device (not shown). 1 and 2) are formed.
Further, a plurality of first communication pipes 52, 52 are arranged in the longitudinal direction so as to penetrate the partition wall 26, one end of which is communicated with the bottom of the outflow water channel 38, and the other end of which is inside the denitrification tank 20. Opened at the bottom. On the other hand, along the other side wall surface in the longitudinal direction of the nitrification tank 28, the inflow channel 5 into which the liquid from the denitrification tank 20 flows.
4 are provided. A plurality of second communication pipes 55 penetrate the partition wall 26 and are arranged in the vertical direction, and one end of the second communication pipe 55 communicates with the bottom of the inflow water channel 54, and the other end of the second communication pipe 55 with an upper part of the denitrification tank 20. It is opened (see FIG. 3). In addition, the pipe 5 from a predetermined position of the inflow water channel 54 to the vicinity of the bottom of the nitrification tank 28
6 is extended, and the tip of the extended pipe 56 is formed sideways or upward so that air from the air diffuser 33 does not enter. As a result, the main body of the device is the partition wall 2
6 is completely partitioned into the nitrification tank 28 and the denitrification tank 20, while the outflow water channel 38, the first communication pipe 52, the second communication pipe 5
5, the inflow water passage 54 and the pipe 56 form a circulation passage for circulating the liquid between the nitrification tank 28 and the denitrification tank 20. In addition, a circulation amount control gate 57 is provided in the inflow water passage 54, whereby the circulation flow rate flowing through the circulation passage can be adjusted according to conditions such as the properties of the raw water and the water temperature. Further, above the liquid surface of the inflow water passage 54, a defoaming device 59 that sprays water on the liquid surface of the inflow water passage 54 is provided (see FIG. 3).

【0021】また、図1、図2、図4に示すように、仕
切壁26の水中攪拌機32上方位置に開口58(図4参
照)が形成されると共に、この開口58から硝化槽28
内を通って大気に通じるダクト60が設けられる。ま
た、仕切壁26の脱窒槽20側面は、ダクト60の開口
58を頂点とした山型状に傾斜して形成される。また、
ダクト60の液面近傍にはスカム回収用の水中ポンプ6
2が設けられると共に、水中ポンプ62はスカム配管6
4(図4参照)により図示しないスカム処理設備に接続
される。これにより、原水16により同伴されて脱窒槽
20の液面に浮上するスカムを回収する。
As shown in FIGS. 1, 2 and 4, an opening 58 (see FIG. 4) is formed in the partition wall 26 at a position above the submersible stirrer 32, and the nitrification tank 28 is opened from this opening 58.
A duct 60 is provided that communicates with the atmosphere through the inside. The side surface of the denitrification tank 20 of the partition wall 26 is formed to be inclined in a mountain shape with the opening 58 of the duct 60 as the apex. Also,
Submersible pump 6 for collecting scum near the liquid surface of duct 60
2 is provided, and the submersible pump 62 is a scum pipe 6
4 (see FIG. 4) is connected to a scum treatment facility (not shown). As a result, the scum that is entrained by the raw water 16 and floats on the liquid surface of the denitrification tank 20 is collected.

【0022】次に、上記の如く構成された本発明の硝化
・脱窒装置14の作用について説明する。図3に示すよ
うに、硝化槽内に設けられた散気装置33からエア66
を硝化槽28内全面に散気して硝化槽28内を好気性に
すると共に、散気によるエアリフト作用により、硝化槽
28内の水位が、嫌気槽12、流出水路38及び流入水
路54に比べて高く(図中h)維持される。これによ
り、硝化槽28内の液は分離スクリーン40を通過して
流出水路38に流れ込む。そして、溢流口50から流出
トラフ48に溢流して硝化・脱窒装置14外に排出され
ると共に、一部の液は、第1の連通管52を下向流とな
って脱窒槽20内に流れ、続いて、脱窒槽20の液は第
2の連通管55を上向流となって流入水路54に流れ込
む。そして、流入水路54に流れ込んだ液は、図4に示
すように配管56を通って硝化槽28の底部に流れ出
る。これにより、硝化槽28と脱窒槽20との間で、循
環流が発生する。この循環流の発生において、第2の連
通管55内にエアリフト作用を発生させる散気管(図示
せず)、或いは第2の連通管55内に上向流を発生させ
るポンプ(図示せず)を設けると、循環をよりスムーズ
に行うことができる。また、循環量の制御は流入水路5
4に設けた循環量制御ゲート57により行うことができ
るので、原水の性状、水温等や昼と夜との原水負荷の違
い等に応じて最適な循環量に制御することができる。
Next, the operation of the nitrification / denitrification apparatus 14 of the present invention constructed as described above will be described. As shown in FIG. 3, air 66 is supplied from the air diffuser 33 provided in the nitrification tank.
Is diffused over the entire surface of the nitrification tank 28 to make the inside of the nitrification tank 28 aerobic, and the water level in the nitrification tank 28 is higher than that of the anaerobic tank 12, the outflow water channel 38 and the inflow water channel 54 due to the air lift action by the air diffusion. Is kept high (h in the figure). As a result, the liquid in the nitrification tank 28 passes through the separation screen 40 and flows into the outflow water channel 38. Then, the liquid overflows from the overflow port 50 to the outflow trough 48 and is discharged to the outside of the nitrification / denitrification device 14, and a part of the liquid flows downward in the first communication pipe 52 into the denitrification tank 20. Then, the liquid in the denitrification tank 20 flows into the inflow water channel 54 as an upward flow through the second communication pipe 55. Then, the liquid flowing into the inflow water channel 54 flows out to the bottom of the nitrification tank 28 through the pipe 56 as shown in FIG. As a result, a circulating flow is generated between the nitrification tank 28 and the denitrification tank 20. In the generation of this circulation flow, an air diffuser (not shown) for generating an air lift action in the second communication pipe 55 or a pump (not shown) for generating an upward flow in the second communication pipe 55 is used. If provided, circulation can be performed more smoothly. In addition, the inflow channel 5 is used to control the circulation amount.
Since it can be controlled by the circulation amount control gate 57 provided in 4, the optimum circulation amount can be controlled according to the characteristics of the raw water, the water temperature, the difference in the raw water load between day and night, and the like.

【0023】このように、本発明の硝化・脱窒装置14
によれば、装置14本体は仕切壁26で硝化槽28と脱
窒槽20とに完全に仕切る一方、硝化槽28に設けた処
理水36の流出水路38と脱窒槽20内とを第1の連通
管52で連通すると共に、脱窒槽20内と硝化槽28に
設けた流入水路54を第2の連通管55で連通し、更に
配管56により硝化槽28内に連通し、散気装置33か
らのエアリフト作用を利用して硝化槽28と脱窒槽20
との間で液を循環させるようにした。これにより、散気
装置33からのエア66、或いは溶存酸素の高い状態の
硝化槽の液が脱窒槽20内に混入しないので、脱窒槽2
0内の液の溶存酸素が高くなるのを防止できる。また、
硝化槽28の液が第1の連通管52内を流れて脱窒槽2
0に下降する間に、液中の気泡が上昇して抜けるので、
脱窒槽20の嫌気状態をより良好に維持できる。更に
は、分離スクリーン40の上方に消泡装置46を設け
て、分離スクリーン40近傍に溜まり易い泡を消泡し、
分離スクリーン40を通過して流出水路38に泡が流れ
込むのを防止するようにした。従って、脱窒槽20内の
嫌気状態が一層良好に維持されるので、脱窒反応を効率
良く行うことができる。
Thus, the nitrification / denitrification apparatus 14 of the present invention
According to the above, the main body of the apparatus 14 completely partitions the nitrification tank 28 and the denitrification tank 20 by the partition wall 26, while the outflow channel 38 of the treated water 36 provided in the nitrification tank 28 and the denitrification tank 20 are connected to each other by the first communication. While communicating with the pipe 52, the inflow water channel 54 provided in the denitrification tank 20 and the nitrification tank 28 are communicated with each other by the second communication pipe 55, and further communicated with the nitrification tank 28 by the pipe 56. The nitrification tank 28 and the denitrification tank 20 using the air lift function
The liquid was circulated between and. As a result, the air 66 from the air diffuser 33 or the liquid of the nitrification tank in a state where the dissolved oxygen is high does not mix into the denitrification tank 20.
It is possible to prevent the dissolved oxygen of the liquid in 0 from increasing. Also,
The liquid in the nitrification tank 28 flows in the first communication pipe 52 and the denitrification tank 2
While falling to 0, the bubbles in the liquid rise and escape,
The anaerobic state of the denitrification tank 20 can be better maintained. Furthermore, a defoaming device 46 is provided above the separation screen 40 to defoam bubbles that easily accumulate near the separation screen 40.
Bubbles were prevented from flowing into the outflow channel 38 through the separating screen 40. Therefore, the anaerobic state in the denitrification tank 20 is more favorably maintained, and the denitrification reaction can be efficiently performed.

【0024】また、本発明の硝化・脱窒装置14は上下
2槽構造になっているので、複数の硝化・脱窒装置1
4、14…を連接させて硝化・脱窒装置14或いは生物
反応装置10の装置本体が長くなっても、硝化槽28と
脱窒槽20との間での液の循環路の長さは変わらない。
これにより、装置10全体が長くなっても循環流量を制
御し易い。また、上下2槽構造にしたことにより、脱窒
槽20の液面が大気と接触する割合が極めて小さくでき
るので、硝化槽28と脱窒槽20とを同一平面に並べた
従来の横型の硝化・脱窒装置に比べ、脱窒槽20の嫌気
度を高めることができる。
Further, since the nitrification / denitrification apparatus 14 of the present invention has an upper and lower two-vessel structure, a plurality of nitrification / denitrification apparatuses 1
The length of the liquid circulation path between the nitrification tank 28 and the denitrification tank 20 does not change even if the apparatus main body of the nitrification / denitrification apparatus 14 or the bioreactor 10 becomes long by connecting 4, 14 ... .
This makes it easy to control the circulation flow rate even if the entire apparatus 10 becomes long. Further, since the upper and lower two-tank structure is used, the ratio of the liquid surface of the denitrification tank 20 in contact with the atmosphere can be made extremely small. The anaerobic degree of the denitrification tank 20 can be increased as compared with the denitrification device.

【0025】また、硝化槽28と脱窒槽20との間の液
の循環を上記の如く構成したので、硝化槽28内全面に
全面散気させることができる。これにより、硝化槽28
内のエアレーションが充分に行われて硝化槽28内が良
好な好気状態に維持されるので、硝化反応を効率良く行
うことができる。因みに、上下2槽構造の従来の縦型の
硝化・脱窒装置の場合、仕切壁26に開放部を形成して
循環させるので、硝化槽28と脱窒槽20との間で旋回
流を発生させる必要があり、この為には硝化槽28全面
の全面散気を行うことができず、硝化槽28内にエアが
充分供給されるエリアと供給されにくいエリアができや
すい欠点がある。
Further, since the liquid circulation between the nitrification tank 28 and the denitrification tank 20 is configured as described above, the entire surface of the nitrification tank 28 can be diffused. As a result, the nitrification tank 28
Since the inside of the nitrification tank 28 is sufficiently aerated and the inside of the nitrification tank 28 is maintained in a favorable aerobic state, the nitrification reaction can be efficiently performed. Incidentally, in the case of a conventional vertical type nitrification / denitrification device having an upper and lower two tank structure, since an opening is formed in the partition wall 26 to circulate it, a swirling flow is generated between the nitrification tank 28 and the denitrification tank 20. Therefore, it is not possible to diffuse the entire surface of the nitrification tank 28, and there are disadvantages that an area where the air is sufficiently supplied and an area where the air is difficult to supply are easily formed in the nitrification tank 28.

【0026】また、脱窒槽20での脱窒反応により、メ
タンガスや窒素ガス等の消化ガスが発生し、この消化ガ
スを装置14外に放出する必要がある。しかし、前記し
た従来の縦型の硝化・脱窒装置の場合、消化ガスが硝化
槽28内を経由してから大気に達するので、大気に放出
されにくいという欠点があると共に、硝化槽28内を経
由することにより硝化反応に悪影響を与える。そこで、
本発明の硝化・脱窒装置14では、仕切壁26の水中攪
拌機32上方位置に開口58を形成し、この開口58か
ら硝化槽28内を通って大気に通じるダクト60を設け
た。また、仕切壁26の脱窒槽20に向いた面は、前記
ダクト60の開口58を頂点とした山型状に傾斜して形
成した。これにより、脱窒槽20でのメタンガスや窒素
ガス等の消化ガスを硝化槽28を通らずに大気に放出で
きるので、硝化槽28での硝化反応を阻害することがな
いと共に、ダクト60は水中攪拌機32の修理等におけ
る搬出路として使用することができる。また、仕切壁2
6の傾斜により、消化ガスがダクト60の入口58に集
まり易くなるので、消化ガスをより速やかに大気に放出
させることができる。
Further, the denitrification reaction in the denitrification tank 20 generates a digestive gas such as methane gas or nitrogen gas, and this digestive gas needs to be discharged to the outside of the apparatus 14. However, in the case of the conventional vertical nitrification / denitrification apparatus described above, digestive gas reaches the atmosphere after passing through the inside of the nitrification tank 28, and thus has the drawback that it is difficult to be released into the atmosphere, and the inside of the nitrification tank 28 By passing through, the nitrification reaction is adversely affected. Therefore,
In the nitrification / denitrification apparatus 14 of the present invention, an opening 58 is formed in the partition wall 26 above the submersible stirrer 32, and a duct 60 is provided from this opening 58 to the atmosphere through the nitrification tank 28. Further, the surface of the partition wall 26 facing the denitrification tank 20 is formed to be inclined in a mountain shape with the opening 58 of the duct 60 as the apex. As a result, digestive gases such as methane gas and nitrogen gas in the denitrification tank 20 can be released to the atmosphere without passing through the nitrification tank 28, so that the nitrification reaction in the nitrification tank 28 is not hindered and the duct 60 serves as an underwater stirrer. It can be used as a carry-out path for repairing 32. Also, the partition wall 2
The inclination of 6 facilitates the digestion gas to collect at the inlet 58 of the duct 60, so that the digestion gas can be released to the atmosphere more quickly.

【0027】本発明の硝化・脱窒装置14によれば、硝
化槽28と脱窒槽20とが同一平面上に並ぶ従来の横型
の硝化・脱窒装置の欠点であった大きな設置スペー
ス、長い循環水路、循環量の制御のしずらさを解決
することができる。また、硝化槽を上階に、脱窒槽を下
階にした従来の縦型の硝化・脱窒装置の欠点であった
硝化槽の良好な好気性条件及び脱窒槽の良好な嫌気性条
件が形成できにくい消化ガスが大気に放出されにくい
という問題を解決することができる。これにより、良好
な硝化・脱窒処理状態を形成でき、且つ循環量の制御が
し易く、しかも装置の省エネ、コンパクト化を図ること
のできる硝化・脱窒装置を提供することができる。
According to the nitrification / denitrification apparatus 14 of the present invention, the nitrification tank 28 and the denitrification tank 20 are arranged on the same plane, which is a drawback of the conventional horizontal nitrification / denitrification apparatus. It is possible to solve the difficulty of controlling the water channel and circulation amount. In addition, a favorable aerobic condition for the nitrification tank and a good anaerobic condition for the denitrification tank were formed, which was a drawback of the conventional vertical nitrification / denitrification equipment with the nitrification tank on the upper floor and the denitrification tank on the lower floor. It is possible to solve the problem that digestive gas that is difficult to make is difficult to be released to the atmosphere. As a result, it is possible to provide a nitrification / denitrification apparatus which can form a favorable nitrification / denitrification treatment state, can easily control the circulation amount, and can save energy and make the apparatus compact.

【0028】尚、本実施例では、硝化槽と脱窒槽との間
の液の循環動力源として散気装置からのエアによるエア
リフト効果を利用した循環で説明したが、これに限定さ
れるものではなく、硝化槽、流出部、流入部の間に予め
水位差を形成してこの水位差を利用しても良く、ポンプ
動力を利用してもよい。
In the present embodiment, the circulation utilizing the air lift effect by the air from the air diffuser as the power source for circulating the liquid between the nitrification tank and the denitrification tank has been described, but the present invention is not limited to this. Alternatively, a water level difference may be previously formed between the nitrification tank, the outflow part, and the inflow part, and this water level difference may be used, or pump power may be used.

【0029】[0029]

【発明の効果】以上説明したように、本発明の硝化・脱
窒装置によれば、次の効果を奏することができる。 従来の横型の硝化・脱窒装置のように大きな設置スペ
ースを必要としない。これにより、装置をコンパクト化
させることができる。
As described above, according to the nitrification / denitrification apparatus of the present invention, the following effects can be obtained. It does not require a large installation space unlike conventional horizontal nitrification / denitrification equipment. As a result, the device can be made compact.

【0030】従来の横型の硝化・脱窒装置のように装
置本体が長くなっても硝化槽と脱窒槽との間の循環路を
長くする必要がない。これにより循環量を制御し易くで
きる。 従来の縦型の硝化・脱窒装置のように、散気装置から
のエアや溶存酸素の高い状態の硝化槽の液が脱窒槽に混
入しない。これにより、脱窒槽には良好な嫌気状態を形
成できる。また、硝化槽と脱窒槽との循環のために旋回
流を発生させる必要がないので、硝化槽内に全面散気で
きる。これにより、硝化槽には良好な好気状態を形成で
きる。更には、硝化槽内に硝化菌を担持した多数の担体
を添加した。従って、硝化・脱窒処理を効率的に行うこ
とができる。
Unlike the conventional horizontal nitrification / denitrification apparatus, it is not necessary to lengthen the circulation path between the nitrification tank and the denitrification tank even if the apparatus main body becomes long. This makes it easier to control the circulation amount. Unlike conventional vertical nitrification / denitrification equipment, the air from the air diffuser and the liquid in the nitrification tank with high dissolved oxygen will not enter the denitrification tank. As a result, a good anaerobic state can be formed in the denitrification tank. Further, since it is not necessary to generate a swirling flow for circulation between the nitrification tank and the denitrification tank, the entire surface can be diffused into the nitrification tank. Thereby, a favorable aerobic condition can be formed in the nitrification tank. Furthermore, many carriers carrying nitrifying bacteria were added to the nitrification tank. Therefore, the nitrification / denitrification treatment can be efficiently performed.

【0031】従来の縦型の硝化・脱窒装置のように、
脱窒槽で発生する消化ガスが硝化槽内を経由して外気に
放出されない。即ち、脱窒槽と外気を結ぶダクトを設け
て、脱窒槽で発生する消化ガスを硝化槽内を経由せずに
外気に放出するようにした。これにより、消化ガスが放
出し易くなると共に、硝化槽を経由しないので硝化反応
に悪影響を与えない。
Like a conventional vertical nitrification / denitrification device,
Digestion gas generated in the denitrification tank is not released to the outside air through the nitrification tank. That is, a duct connecting the denitrification tank and the outside air was provided so that the digested gas generated in the denitrification tank was released to the outside air without passing through the nitrification tank. As a result, the digestive gas is easily released, and since it does not pass through the nitrification tank, it does not adversely affect the nitrification reaction.

【0032】散気装置からのエアリフト作用を利用し
て硝化槽と脱窒槽との間で液を循環するようにした。こ
れにより、省エネを図ることができる。
The liquid was circulated between the nitrification tank and the denitrification tank by utilizing the air lift action from the air diffuser. Thereby, energy saving can be achieved.

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

【図1】図1は、嫌気槽と本発明の硝化・脱窒装置とを
組み合わせて、生物学的にリン成分・窒素成分の同時除
去を行う生物反応装置の内部構造を示す断面図
FIG. 1 is a cross-sectional view showing the internal structure of a biological reaction apparatus for biologically simultaneously removing phosphorus components and nitrogen components by combining an anaerobic tank and the nitrification / denitrification apparatus of the present invention.

【図2】図2は、本発明の硝化・脱窒装置を上側(硝化
槽側)から見た平面図
FIG. 2 is a plan view of the nitrification / denitrification apparatus of the present invention viewed from the upper side (nitrification tank side).

【図3】図3は図2のA−A線に沿った縦断面図3 is a longitudinal sectional view taken along the line AA of FIG.

【図4】図4は図2のB−B線に沿った縦断面図4 is a vertical cross-sectional view taken along the line BB of FIG.

【符号の説明】[Explanation of symbols]

10…生物反応装置 14…硝化・脱窒装置 16…原水 18…原水配管 20…脱窒槽 26…仕切壁 28…硝化槽 30…担体 22、32…水中攪拌機 33…散気装置 34…散気装置の吹出口 36…処理水 38…流出水路 40…分離スクリーン 48…流出トラフ 50…溢流口 52…第1の連通管 54…流入水路 55…第2の連通管 56…配管 58…ダクトの開口 60…ダクト 66…エア 10 ... Biological reaction device 14 ... Nitrification / denitrification device 16 ... Raw water 18 ... Raw water pipe 20 ... Denitrification tank 26 ... Partition wall 28 ... Nitrification tank 30 ... Carrier 22, 32 ... Submersible agitator 33 ... Diffuser 34 ... Diffuser Outlet 36 ... Treated water 38 ... Outflow water channel 40 ... Separation screen 48 ... Outflow trough 50 ... Overflow port 52 ... First communication pipe 54 ... Inflow water passage 55 ... Second communication pipe 56 ... Piping 58 ... Duct opening 60 ... Duct 66 ... Air

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/30 ZAB A (72)発明者 小 島 正 行 東京都千代田区内神田1丁目1番14号 日 立プラント建設株式会社内 (72)発明者 川 尻 斉 東京都千代田区内神田1丁目1番14号 日 立プラント建設株式会社内 (72)発明者 北 沢 照 啓 東京都千代田区内神田1丁目1番14号 日 立プラント建設株式会社内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI technical display location C02F 3/30 ZAB A (72) Inventor Masayuki Kojima 1-1-1 Uchikanda, Chiyoda-ku, Tokyo No. 14 Hijiri Plant Construction Co., Ltd. (72) Inventor Hitoshi Kawajiri 1-1-14 Kanda, Uchida, Chiyoda-ku, Tokyo Tokyo Plant Construction Co., Ltd. (72) Inventor Teruaki Kitazawa Within Chiyoda-ku, Tokyo 1-14 Kanda 1-Nitta Plant Construction Co., Ltd.

Claims (8)

【特許請求の範囲】[Claims] 【請求項1】仕切壁により上下2槽に仕切って、原水流
入口を有する脱窒槽を下階に形成すると共に、処理水の
流出水路を有する硝化槽を上階に形成した装置本体と、 前記硝化槽内に添加され、硝化菌を担持した多数の担体
と、 前記流出水路に一方の開口が連通されると共に、前記脱
窒槽内に他方の開口が形成される第1の連通管と、 前記脱窒槽内に一方の開口が形成されると共に、前記硝
化槽内又は硝化槽に近接して設けられ硝化槽内に通じる
流入水路に他方の開口が連通される第2の連通管と、 前記硝化槽の底部に設けられ、硝化槽内にエアを散気す
る散気装置と、 から成り、前記硝化槽と前記脱窒槽との間で、前記流出
水路、前記第1の配管、前記第2の配管、前記流入水路
の順路で液を循環させることを特徴とする硝化・脱窒装
置。
1. An apparatus main body having a denitrification tank having a raw water inlet port formed on a lower floor and a nitrification tank having a treated water outflow passage formed on an upper floor, which is divided into upper and lower tanks by a partition wall. A large number of carriers that are added to the nitrification tank and carry nitrifying bacteria, and a first communication pipe in which one opening is connected to the outflow water channel and the other opening is formed in the denitrification tank, A second communication pipe having one opening formed in the denitrification tank and having the other opening communicated with an inflow water channel which is provided in the nitrification tank or close to the nitrification tank and communicates with the nitrification tank. An air diffuser provided at the bottom of the tank for diffusing air into the nitrification tank, and between the nitrification tank and the denitrification tank, the outflow water channel, the first pipe, and the second pipe. Nitrification / denitrification equipment characterized by circulating a liquid through the piping and the inflow channel .
【請求項2】前記散気装置によるエアリフト作用により
前記硝化槽と前記脱窒槽との間で液を循環させることを
特徴とする請求項1の硝化・脱窒装置。
2. The nitrification / denitrification apparatus according to claim 1, wherein a liquid is circulated between the nitrification tank and the denitrification tank by an air lift action of the air diffuser.
【請求項3】前記第2の連通管内にエアリフト作用を発
生させる散気管が設けられていることを特徴とする請求
項1の硝化・脱窒装置。
3. The nitrification / denitrification apparatus according to claim 1, wherein an air diffusing pipe for generating an air lift action is provided in the second communicating pipe.
【請求項4】前記第2の連通管内に上向流を発生させる
ポンプが設けられていることを特徴とする請求項1の硝
化・脱窒装置。
4. The nitrification / denitrification apparatus according to claim 1, further comprising a pump for generating an upward flow in the second communicating pipe.
【請求項5】前記流入水路には前記順路で循環する液の
循環量を制御する制御手段が設けられていることを特徴
とする請求項1の硝化・脱窒装置。
5. The nitrification / denitrification apparatus according to claim 1, wherein the inflow water channel is provided with control means for controlling the circulation amount of the liquid circulating in the forward path.
【請求項6】前記脱窒槽内には攪拌装置が設けられると
共に、前記仕切壁の前記攪拌装置上方位置に形成した開
口から前記硝化槽を通って外気に通じるダクトを設けた
ことを特徴とする請求項1の硝化・脱窒装置。
6. The denitrification tank is provided with a stirrer, and a duct is provided through an opening formed at a position above the stirrer of the partition wall to pass through the nitrification tank to the outside air. The nitrification / denitrification apparatus according to claim 1.
【請求項7】前記仕切壁の脱窒槽側面は、前記ダクトの
開口を頂点とした傾斜が形成されることを特徴とする請
求項1の硝化・脱窒装置。
7. The nitrification / denitrification apparatus according to claim 1, wherein a side surface of the partition wall of the denitrification tank is inclined with the opening of the duct as an apex.
【請求項8】前記流出水路近傍には、流出水路に流れ込
む液の泡を消す消泡装置が設けられていることを特徴と
する請求項1の硝化・脱窒装置。
8. The nitrification / denitrification apparatus according to claim 1, further comprising a defoaming device provided near the outflow channel for eliminating bubbles of the liquid flowing into the outflow channel.
JP15227294A 1994-07-04 1994-07-04 Nitrification / denitrification equipment Expired - Lifetime JP3223945B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15227294A JP3223945B2 (en) 1994-07-04 1994-07-04 Nitrification / denitrification equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15227294A JP3223945B2 (en) 1994-07-04 1994-07-04 Nitrification / denitrification equipment

Publications (2)

Publication Number Publication Date
JPH0810793A true JPH0810793A (en) 1996-01-16
JP3223945B2 JP3223945B2 (en) 2001-10-29

Family

ID=15536882

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15227294A Expired - Lifetime JP3223945B2 (en) 1994-07-04 1994-07-04 Nitrification / denitrification equipment

Country Status (1)

Country Link
JP (1) JP3223945B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100760816B1 (en) * 2007-03-02 2007-10-04 최광회 Advanced wastewater treatment process using up & down aerobic??anaerobic basin of channel type in a unit basin with recycle
JP2008194620A (en) * 2007-02-13 2008-08-28 Hitachi Plant Technologies Ltd Wastewater treating method and apparatus
JP2015525667A (en) * 2012-07-06 2015-09-07 リ ジンミンLI, Jinmin Biological sewage treatment apparatus and method
WO2020071173A1 (en) * 2018-10-04 2020-04-09 株式会社クボタ Organic wastewater treatment apparatus
WO2023026837A1 (en) * 2021-08-23 2023-03-02 株式会社クボタ Multitiered treatment tank and sewage treatment system

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008194620A (en) * 2007-02-13 2008-08-28 Hitachi Plant Technologies Ltd Wastewater treating method and apparatus
KR100760816B1 (en) * 2007-03-02 2007-10-04 최광회 Advanced wastewater treatment process using up & down aerobic??anaerobic basin of channel type in a unit basin with recycle
WO2008108546A1 (en) * 2007-03-02 2008-09-12 Kwang Hoe Choi Advanced wastewater treatment process using up & down aerobic • anaerobic reactors of channel type.
US7972507B2 (en) 2007-03-02 2011-07-05 Kwang Hoe Choi Advanced wastewater treatment process using up and down aerobic/anaerobic reactors of channel type
JP2015525667A (en) * 2012-07-06 2015-09-07 リ ジンミンLI, Jinmin Biological sewage treatment apparatus and method
WO2020071173A1 (en) * 2018-10-04 2020-04-09 株式会社クボタ Organic wastewater treatment apparatus
JP2020054980A (en) * 2018-10-04 2020-04-09 株式会社クボタ Organic wastewater treatment apparatus
US11731891B2 (en) 2018-10-04 2023-08-22 Kubota Corporation Organic wastewater treatment apparatus
WO2023026837A1 (en) * 2021-08-23 2023-03-02 株式会社クボタ Multitiered treatment tank and sewage treatment system

Also Published As

Publication number Publication date
JP3223945B2 (en) 2001-10-29

Similar Documents

Publication Publication Date Title
JP5665307B2 (en) Organic waste water treatment apparatus and organic waste water treatment method
KR19990021838A (en) Aerobic treatment method and treatment tank of sewage
CN111138024B (en) Integrated vertical circulating reactor for nitrogen and phosphorus removal of sewage
CN106946355B (en) Jet aeration type A/O integrated sewage treatment device and sewage treatment process thereof
CN206970300U (en) Nitrification liquid reflux and biological reaction pool for biological reaction pool
CN114604971B (en) BioDopp biochemical reaction system for reinforcing biological phosphorus removal and sewage treatment method
CN207986809U (en) The AAO biochemical treatment tanks of treated sewage
CN110510815B (en) Integrated sewage treatment device based on simultaneous nitrification and denitrification and sewage treatment method
KR101304329B1 (en) Micro Bubble Reactor for Treatment of Wastewater Using Micro Bubble Diffuser With Cleaning Function
JP3223945B2 (en) Nitrification / denitrification equipment
JP3150530B2 (en) Biological nitrogen removal equipment
CN214270604U (en) Single-power sewage treatment system and sewage treatment tank thereof
CN210764579U (en) Sewage treatment system
KR100304058B1 (en) Reactor tank bulkhead and sewage treatment system used in sewage treatment system
SK101195A3 (en) Method and apparatus for biological activation waste water treatment and device for its realization
CN207313241U (en) A kind of micro- oxygen denitrification reactor of cavitation-preventive
JP2000301184A (en) Nitrogen removing apparatus
JP3220927B2 (en) Nitrification / denitrification equipment
JP3116323B2 (en) Merged septic tank
KR100540549B1 (en) An Apparatus for Advanced Wastewater Treatment Using Vertical Type Membrane Bio-Reactor
JPS6068097A (en) Removing apparatus of n and p in sewage
CN215480024U (en) Self-circulation continuous flow two-oxygen composite granular sludge purification treatment device
CN219972037U (en) Integrated biological reaction tank reflux system and aeration system
CN114105297B (en) Continuous flow self-circulation aerobic granular sludge processor
CN213652010U (en) Sewage treatment device

Legal Events

Date Code Title Description
S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080824

Year of fee payment: 7

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090824

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090824

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100824

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100824

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110824

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120824

Year of fee payment: 11

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130824

Year of fee payment: 12

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313115

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

EXPY Cancellation because of completion of term