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JPS635838Y2 - - Google Patents

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Publication number
JPS635838Y2
JPS635838Y2 JP5184882U JP5184882U JPS635838Y2 JP S635838 Y2 JPS635838 Y2 JP S635838Y2 JP 5184882 U JP5184882 U JP 5184882U JP 5184882 U JP5184882 U JP 5184882U JP S635838 Y2 JPS635838 Y2 JP S635838Y2
Authority
JP
Japan
Prior art keywords
tank
water
denitrification
biological treatment
gas discharge
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.)
Expired
Application number
JP5184882U
Other languages
Japanese (ja)
Other versions
JPS58156597U (en
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 filed Critical
Priority to JP5184882U priority Critical patent/JPS58156597U/en
Publication of JPS58156597U publication Critical patent/JPS58156597U/en
Application granted granted Critical
Publication of JPS635838Y2 publication Critical patent/JPS635838Y2/ja
Granted legal-status Critical Current

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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【考案の詳細な説明】 本考案はし尿、下水その他有機性廃水などを微
生物によつて硝化脱窒処理するための生物学的脱
窒素槽に関するものである。
[Detailed Description of the Invention] The present invention relates to a biological denitrification tank for nitrifying and denitrifying human waste, sewage, and other organic wastewater using microorganisms.

一般に、この種の有機性廃水の生物学的硝化脱
窒処理は、廃水の窒素分(以下NH3と略する)
を好気的条件下で硝化してNOx(NO2 or/and
NO3)としたのち、嫌気的条件下でNOxをN2
スにまで還元分解(脱窒)して水中から放散する
ものである。従つてこの処理用の脱窒素槽は嫌気
的条件を維持するため密閉構造となつており、
N2ガスは水封されたガス放出部から放出される。
In general, this kind of biological nitrification and denitrification treatment of organic wastewater reduces the nitrogen content (hereinafter abbreviated as NH3 ) of wastewater.
is nitrified under aerobic conditions to produce NOx (NO 2 or/and
NOx ) is then reduced and decomposed (denitrified) to N2 gas under anaerobic conditions and released from the water. Therefore, the denitrification tank for this treatment has a sealed structure to maintain anaerobic conditions.
N2 gas is released from a water-sealed gas release section.

従来の脱窒素槽に設けられるガス放出部は第1
図に示す如く脱窒素槽Aの頂面に連結したガス放
出管Bを水封水貯槽Cに設けたガス放出塔D内に
連通状態で配備し、ガス放出塔D中にガス洗浄機
構Eを設けた複雑な構造となつていて、該ガス放
出塔D内ではN2ガス中に混在している悪臭ガス
を除去するため水滴を向流に接触しているものも
ある。しかしながらこのようなガス放出部は 脱窒素槽A中で発泡すると、泡がガス放出塔
Dまで上昇し、水封水槽C上に溢れ出て脱窒素
槽A上を著しく汚染する。またガス放出管Bが
泡によつて閉塞、内放を繰り返すことによつて
脱窒素槽Aの内圧が増減し、液位が変化する。
従つて沈殿槽流入混合液が脈流となり、沈殿槽
の水量負荷が変化し、その機能を損う。
The gas discharge section provided in the conventional denitrification tank is the first
As shown in the figure, a gas discharge pipe B connected to the top surface of the denitrification tank A is placed in communication with a gas discharge tower D provided in a water seal storage tank C, and a gas cleaning mechanism E is installed in the gas discharge tower D. In some cases, the gas release tower D has a complicated structure in which water droplets are brought into contact with each other in a countercurrent direction in order to remove the foul-smelling gas mixed in the N 2 gas. However, when such a gas discharge section generates bubbles in the denitrification tank A, the bubbles rise to the gas discharge tower D and overflow onto the water seal tank C, contaminating the top of the denitrification tank A significantly. Further, as the gas discharge pipe B is repeatedly blocked by bubbles and discharged inward, the internal pressure of the denitrification tank A increases and decreases, and the liquid level changes.
Therefore, the mixed liquid flowing into the sedimentation tank becomes a pulsating flow, and the water load on the sedimentation tank changes, impairing its function.

構造が複雑なので建設が繁雑となり設備費が
嵩さむなどの欠点があつた。
The structure was complicated, so construction was complicated and equipment costs were high.

本考案は、これら従来の欠点を排除することを
目的とするもので、ガス放出を適確、安全に行な
い硝化脱窒処理を効率よく行なうことができ、脱
窒素槽に生ずる泡の処理も容易で沈殿槽の機能を
良好に維持できる構成簡単で安価な生物処理装置
を提供することにある。
The purpose of this invention is to eliminate these conventional drawbacks, and it is possible to perform nitrification and denitrification treatment efficiently by accurately and safely releasing gas, and it is also easy to dispose of bubbles that occur in the denitrification tank. An object of the present invention is to provide a biological treatment device with a simple configuration and low cost, which can maintain the functions of a sedimentation tank well.

本考案は、脱窒素槽と好気性槽が配備された生
物学的硝化脱窒素装置において、該脱窒素槽の気
相部の側壁に余剰ガスを排出する中空構造体が取
付けられ、該中空構造体の先端が前記好気性槽に
配備された水封水貯槽の液に浸漬されたものであ
ることを特徴とする生物処理装置である。
The present invention provides a biological nitrification and denitrification device equipped with a denitrification tank and an aerobic tank, in which a hollow structure for discharging surplus gas is attached to the side wall of the gas phase section of the denitrification tank, and the hollow structure This biological treatment device is characterized in that the tip of the body is immersed in the liquid of a water-sealed water storage tank provided in the aerobic tank.

本考案を第2図乃至第8図に基いて説明する。
第2図乃至第6図及び第8図は、槽を仕切壁4で
二槽に区画形成し、一方を好気性槽である硝化槽
1、他方を嫌気槽である脱窒素槽2としてある。
脱窒素槽2は嫌気状態を維持するため蓋部で大気
と遮断されており、該脱窒素槽2で発生するN2
ガスや泡などを放出するガス放出部として中空構
造体からなるガス放出筒3を気相部側壁に下方向
に開口連設してあり、ガス放出筒3の開放先端で
あるガス放出口3′は水封水貯槽5の液中に開口
配備してある。第2図乃至第5図においては水封
水貯槽5は硝化槽1内の角部に仕切壁4と槽壁と
を側部として区画形成されていて(第8図参照)、
第2図では溢流した水封水が硝化槽1内に流出す
る高さで硝化槽1内に設けられ、第3図では硝化
槽1内の液中に没し該液を水封水として構成され
ている。
The present invention will be explained based on FIGS. 2 to 8.
In FIGS. 2 to 6 and 8, the tank is divided into two tanks by a partition wall 4, one of which is a nitrification tank 1 which is an aerobic tank, and the other is a denitrification tank 2 which is an anaerobic tank.
The denitrification tank 2 is isolated from the atmosphere by a lid to maintain an anaerobic state, and the N 2 generated in the denitrification tank 2 is
A gas discharge tube 3 made of a hollow structure is provided as a gas discharge section for discharging gas, bubbles, etc. and is opened downward in a continuous manner on the side wall of the gas phase section, and the open end of the gas discharge tube 3 is a gas discharge port 3'. is opened into the liquid of the water seal water storage tank 5. In FIGS. 2 to 5, the water seal water storage tank 5 is formed at a corner of the nitrification tank 1 with the partition wall 4 and the tank wall as sides (see FIG. 8).
In Fig. 2, the overflowing water seal water is provided in the nitrification tank 1 at a height where it flows into the nitrification tank 1, and in Fig. 3, it is submerged in the liquid in the nitrification tank 1 and the liquid is used as water seal water. It is configured.

第4図では硝化槽1の液面より上部に設けられ
ているが、いずれの場合も硝化槽1内の液面の変
動により生じうる相対的設置高さであり、作用効
果上顕著な差異はないものの、ガス放出筒3の先
端であるガス放出口3′の高さが水封水貯槽5の
脱窒素槽2側液面高さとなるようにし、ガス放出
口3′高さ、水封水貯槽5の大気側側壁の高さ、
水封水量等の調整水封水貯槽5の脱窒素槽2側液
面と大気側液面との高さの差が300mm以下好まし
くは50〜100mmとなるようにするのが発生するガ
スや泡を放出させ易く脱窒素槽2内の内圧上昇に
よる液面低下で生じる有効容積の減少を防ぐのに
効果的である。
In Fig. 4, it is installed above the liquid level in the nitrification tank 1, but in either case, this is a relative installation height that may occur due to fluctuations in the liquid level in the nitrification tank 1, and there is no noticeable difference in operation and effect. However, the height of the gas discharge port 3', which is the tip of the gas discharge cylinder 3, is set to be equal to the liquid level on the denitrification tank 2 side of the water seal water storage tank 5, and the height of the gas discharge port 3' and the water seal water storage tank 5 are The height of the atmospheric side wall of the storage tank 5,
Adjustment of water seal water volume, etc. The difference in height between the liquid level on the denitrification tank 2 side of the water seal water storage tank 5 and the liquid level on the atmospheric side should be 300 mm or less, preferably 50 to 100 mm. It is effective in preventing a decrease in the effective volume caused by a drop in the liquid level due to an increase in internal pressure in the denitrification tank 2.

第6図では水封水貯槽5は適宜支承手段により
硝化槽1液面上に配備された例、第7図では隣接
する硝化槽1と脱窒素槽2の二槽間に配備した例
である。
Fig. 6 shows an example in which the water-sealed water storage tank 5 is placed above the liquid level of the nitrification tank 1 using appropriate supporting means, and Fig. 7 shows an example in which it is placed between two adjacent tanks, the nitrification tank 1 and the denitrification tank 2. .

前記ガス放出筒3は第2図乃至第5図に示すよ
うに蓋部や仕切壁4の垂直上部を筒壁として構成
してもよいし、第6図及び第7図のように筒体を
付設してもよいが、いずれにしても槽壁のガス放
出筒3開口が気相部の中間高さ部分を含む側壁部
位に設けるのがよく、その内径を100mm以上好ま
しくは200〜1000mm程度とし、水封水貯槽5の底
板とガス放出口3′の間隙を少なくとも100mm以上
とするのが発生した泡でガスの放出路が閉塞され
るのを防止するのに有効である。
The gas discharge cylinder 3 may have a lid or a vertical upper part of the partition wall 4 as a cylinder wall as shown in FIGS. 2 to 5, or a cylinder body as shown in FIGS. 6 and 7. However, in any case, it is preferable that the opening of the gas discharge tube 3 in the tank wall be provided in the side wall part including the middle height part of the gas phase part, and the inner diameter should be 100 mm or more, preferably about 200 to 1000 mm. It is effective to make the gap between the bottom plate of the water seal water storage tank 5 and the gas discharge port 3' at least 100 mm or more to prevent the gas discharge path from being blocked by generated bubbles.

また前記水封水貯槽5に保持される水封水とし
ては硝化槽1や脱窒素槽2中の被処理液、水道水
等が用いられる。
The water to be treated in the nitrification tank 1 and the denitrification tank 2, tap water, etc. are used as the water to be held in the water to the water storage tank 5.

図中6は泡、7は連通口、8は曝気用ブロワ、
9は散気管、10は脱窒素槽2内撹拌用のガス配
管、11はガス吸引口で脱窒素槽2に開口したガ
ス放出筒3よりも上方に設けて泡を吸引すること
のないようにしてある。12は撹拌用ブロワ、1
3はガス噴出管、14は水封水補給路、15はポ
ンプ、16は連絡管である。
In the figure, 6 is foam, 7 is a communication port, 8 is an aeration blower,
9 is an aeration pipe, 10 is a gas pipe for stirring inside the denitrification tank 2, and 11 is a gas suction port, which is installed above the gas discharge tube 3 that opens into the denitrification tank 2 to prevent bubbles from being sucked in. There is. 12 is a stirring blower, 1
3 is a gas ejection pipe, 14 is a water seal water supply path, 15 is a pump, and 16 is a communication pipe.

上述の二槽における被処理液の流過順序は生物
学的硝化脱窒素装置において採用される、例えば
第1脱窒素槽から硝化槽、硝化槽から脱窒素槽、
あるいは槽間を循環させるものであり、好気性槽
が脱窒処理済液が流入する再曝気槽の場合もあ
る。
The flow order of the treated liquid in the two tanks described above is adopted in a biological nitrification and denitrification device, for example, from the first denitrification tank to the nitrification tank, from the nitrification tank to the denitrification tank, and so on.
Alternatively, the aerobic tank may be a reaeration tank into which the denitrified liquid flows.

さらに水封水貯槽を好気性槽とは関連配備する
ことなく別個に設けた場合、あるいは単独に設け
られた嫌気槽の場合など、ガス放出筒を側壁から
下方向に向けて配備し先端を水封構造とすること
により泡による閉塞で槽内内圧の上昇が起ること
を防止でき円滑にガスや泡の放出が行われるもの
である。
Furthermore, when the water seal water storage tank is installed separately from the aerobic tank, or when the anaerobic tank is installed independently, the gas discharge tube is placed downward from the side wall and the tip is placed in the water. The sealing structure prevents an increase in internal pressure in the tank due to blockage caused by bubbles, and allows gas and bubbles to be smoothly released.

本考案により、脱窒素槽で発生する窒素ガスや
泡を円滑に槽外に排除して生物処理を効率的にし
かも安定した状態で行なえる装置を構成簡単安価
に提供でき、実用上大なる効果を有するものであ
る。
With this invention, it is possible to provide a simple and inexpensive device that can smoothly eliminate nitrogen gas and bubbles generated in a denitrification tank to perform biological treatment efficiently and in a stable state, and has great practical effects. It has the following.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は従来例の縦断面図、第2図は本考案の
実施例を示す縦断面図、第3図及び第4図は他の
実施例の縦断面図、第5図はその平面図、第6図
及び第7図はさらに他の実施例の一部の縦断面
図、第8図は一部の斜面図である。 1……硝化槽、2……脱窒素槽、3……ガス放
出筒、4……仕切壁、5……水封水貯槽。
Fig. 1 is a longitudinal sectional view of a conventional example, Fig. 2 is a longitudinal sectional view showing an embodiment of the present invention, Figs. 3 and 4 are longitudinal sectional views of other embodiments, and Fig. 5 is a plan view thereof. , FIG. 6 and FIG. 7 are longitudinal cross-sectional views of a part of still another embodiment, and FIG. 8 is a partial perspective view of another embodiment. 1... Nitrification tank, 2... Denitrification tank, 3... Gas discharge tube, 4... Partition wall, 5... Water seal water storage tank.

Claims (1)

【実用新案登録請求の範囲】 1 脱窒素槽と好気性槽とを備えた生物学的硝化
脱窒素装置において、前記脱窒素槽のガス放出
部を前記好気性槽に配備された水封水貯槽の水
面下に浸漬して成る生物処理装置。 2 前記ガス放出部が、脱窒素槽の気相部側壁に
連設した中空構造体であつて該中空構造体の先
端を水封水貯槽の水面下に浸漬したものである
実用新案登録請求の範囲第1項記載の生物処理
装置。 3 前記水封水貯槽が、前記好気性槽の液に接触
しているように水面下に配備された水槽である
実用新案登録請求の範囲第1項又は第2項記載
の生物処理装置。 4 前記水封水貯槽が、前記好気性槽の水面上に
配備された水槽である実用新案登録請求の範囲
第1項又は第2項記載の生物処理装置。 5 前記水封水貯槽が、前記脱窒素槽又は好気性
槽の液を注入できる水封水補給路を備えたもの
である実用新案登録請求の範囲第1項,第2項
又は第4項記載の生物処理装置。 6 前記好気性槽が、硝化槽又は再曝気槽である
実用新案登録請求の範囲第2項,第3項,第4
項又は第5項記載の生物処理装置。
[Claims for Utility Model Registration] 1. In a biological nitrification and denitrification device equipped with a denitrification tank and an aerobic tank, the gas discharge part of the denitrification tank is connected to a water-sealed water storage tank provided in the aerobic tank. A biological treatment device that is submerged under the water surface. 2. A utility model registration claim in which the gas discharge part is a hollow structure connected to the side wall of the gas phase part of the denitrification tank, and the tip of the hollow structure is immersed under the water surface of the water seal water storage tank. Biological treatment equipment according to scope 1. 3. The biological treatment apparatus according to claim 1 or 2, wherein the water seal water storage tank is a water tank arranged below the water surface so as to be in contact with the liquid in the aerobic tank. 4. The biological treatment apparatus according to claim 1 or 2, wherein the sealed water storage tank is a water tank placed above the water surface of the aerobic tank. 5. Claims 1, 2, or 4 of the registered utility model, wherein the water seal water storage tank is equipped with a water seal water supply channel into which liquid from the denitrification tank or aerobic tank can be poured. biological treatment equipment. 6 Claims 2, 3, and 4 for utility model registration in which the aerobic tank is a nitrification tank or a reaeration tank
The biological treatment device according to item 1 or 5.
JP5184882U 1982-04-12 1982-04-12 Biological treatment equipment Granted JPS58156597U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5184882U JPS58156597U (en) 1982-04-12 1982-04-12 Biological treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5184882U JPS58156597U (en) 1982-04-12 1982-04-12 Biological treatment equipment

Publications (2)

Publication Number Publication Date
JPS58156597U JPS58156597U (en) 1983-10-19
JPS635838Y2 true JPS635838Y2 (en) 1988-02-17

Family

ID=30062555

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5184882U Granted JPS58156597U (en) 1982-04-12 1982-04-12 Biological treatment equipment

Country Status (1)

Country Link
JP (1) JPS58156597U (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0824918B2 (en) * 1991-07-06 1996-03-13 日本碍子株式会社 Aeration tank for anaerobic / aerobic treatment and scum outflow method in this aeration tank

Also Published As

Publication number Publication date
JPS58156597U (en) 1983-10-19

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