JPH0478358B2 - - Google Patents

Info

Publication number
JPH0478358B2
JPH0478358B2 JP62266523A JP26652387A JPH0478358B2 JP H0478358 B2 JPH0478358 B2 JP H0478358B2 JP 62266523 A JP62266523 A JP 62266523A JP 26652387 A JP26652387 A JP 26652387A JP H0478358 B2 JPH0478358 B2 JP H0478358B2
Authority
JP
Japan
Prior art keywords
tank
gas
wastewater treatment
nitrogen
wastewater
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 - Lifetime
Application number
JP62266523A
Other languages
Japanese (ja)
Other versions
JPH01111492A (en
Inventor
Akiji Miura
Hirokazu Tsuji
Yukimasa Ogawa
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.)
OOBAYASHIGUMI KK
OOSAKA GASU KK
Original Assignee
OOBAYASHIGUMI KK
OOSAKA GASU KK
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 OOBAYASHIGUMI KK, OOSAKA GASU KK filed Critical OOBAYASHIGUMI KK
Priority to JP62266523A priority Critical patent/JPH01111492A/en
Publication of JPH01111492A publication Critical patent/JPH01111492A/en
Publication of JPH0478358B2 publication Critical patent/JPH0478358B2/ja
Granted 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

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

Description

【発明の詳細な説明】 ≪産業上の利用分野≫ この発明は、窒素を含有する有機性の各種廃水
(都市下水、生活廃水、食品工場・化学工場・パ
ルプ工場等からの工場廃水、畜産廃水等)を処理
する深層型廃水処理装置に関し、特に、硝化槽か
ら廃水処理液を脱窒槽にリターンさせる場合にお
いて、脱窒槽の嫌気状態を容易に維持できる深層
型廃水処理装置に関するものである。
[Detailed Description of the Invention] <<Industrial Application Field>> This invention is applicable to various types of organic wastewater containing nitrogen (urban sewage, domestic wastewater, industrial wastewater from food factories, chemical factories, pulp factories, etc., livestock wastewater). The present invention relates to a deep-layer wastewater treatment device that processes wastewater (e.g.), and in particular, to a deep-layer wastewater treatment device that can easily maintain an anaerobic state in the denitrification tank when the wastewater treatment liquid is returned from the nitrification tank to the denitrification tank.

≪従来の技術≫ 周知のように、廃水処理装置の一種として、活
性汚泥法が有り、この方法では、活性汚泥と呼ば
れる微生物を利用して廃水中の有機物を分解する
生物化学的な処理を行う。
<<Prior art>> As is well known, there is an activated sludge method as a type of wastewater treatment equipment, and this method uses microorganisms called activated sludge to perform biochemical treatment to decompose organic matter in wastewater. .

このような廃水処理方法では、処理槽に収容し
た廃水源液を酸素ないしは空気で曝気する必要が
あるが、処理槽を横形にすると、設置面積が大き
くなるとともに、廃水源液に溶存する酸素量が限
られるので、例えば、特公昭59−38031号公報に
開示されているように、処理槽を40m以下の地下
に設置した深層型の廃水処理装置が提案されてい
る。
In such wastewater treatment methods, it is necessary to aerate the wastewater source liquid stored in the treatment tank with oxygen or air, but if the treatment tank is made horizontal, the installation area becomes larger and the amount of oxygen dissolved in the wastewater source liquid is reduced. For this reason, for example, as disclosed in Japanese Patent Publication No. 59-38031, a deep type wastewater treatment device in which a treatment tank is installed underground at a depth of 40 m or less has been proposed.

ところで、この種の深層型廃水処理装置とし
て、廃水中の窒素を除去するものとして、従来第
2図に示すように装置がある。
By the way, as a deep-layer wastewater treatment apparatus of this type, there is a conventional apparatus shown in FIG. 2 that removes nitrogen from wastewater.

同図に示す廃水処理装置は、縦形の脱窒槽1
と、硝化槽2とを設置し、脱窒槽1内を嫌気状態
に維持するとともに、硝化槽2内には酸素を供給
して曝気し、硝化槽2内は好気状態に維持する。
The wastewater treatment equipment shown in the figure consists of a vertical denitrification tank 1
and a nitrification tank 2 are installed, and the inside of the denitrification tank 1 is maintained in an anaerobic state, and the inside of the nitrification tank 2 is aerated by supplying oxygen, so that the inside of the nitrification tank 2 is maintained in an aerobic state.

そして、硝化槽2と脱窒槽1とは、リターン通
路3で接続される。
The nitrification tank 2 and the denitrification tank 1 are connected through a return passage 3.

この廃水処理装置では、脱窒には必要な炭素源
は流入廃水中の有機物を利用するため、外部から
メタノールを供給する必要がないという利点があ
り、脱窒槽1に廃水原液を供給すると、廃水原液
中のアンモニヤ性窒素が硝化槽2で曝気されるこ
とにより硝酸性の窒素に変わり、これがふたたび
リターン通路3を介して脱窒槽1に戻されると、
槽1内の微生物の作用により窒素ガスとして除去
されることになるが、この場合に以下に説明する
問題があつた。
This wastewater treatment equipment has the advantage that there is no need to supply methanol from the outside because the carbon source necessary for denitrification uses organic matter in the inflowing wastewater. Ammonia nitrogen in the stock solution is aerated in the nitrification tank 2 and turns into nitrate nitrogen, which is then returned to the denitrification tank 1 via the return passage 3.
The nitrogen gas is removed as nitrogen gas by the action of microorganisms in the tank 1, but in this case, the following problems arose.

≪発明が解決しようとする問題点≫ すなわち、第2図に示した廃水処理装置では、
脱窒槽1は嫌気状態に維持されているが、リター
ン通路3を介して循環される処理液は、好気状態
の硝化槽2から導入されるので、当然のことなが
ら溶存酸素をかなり含んでいる。
≪Problems to be solved by the invention≫ In other words, in the wastewater treatment device shown in Fig. 2,
The denitrification tank 1 is maintained in an anaerobic state, but since the treated liquid circulated through the return passage 3 is introduced from the nitrification tank 2 in an aerobic state, it naturally contains a considerable amount of dissolved oxygen. .

従つて、これをそのまま供給すると脱窒槽1内
を嫌気状態に維持することが難しくなる。
Therefore, if this is supplied as is, it will be difficult to maintain the inside of the denitrification tank 1 in an anaerobic state.

特に、硝化槽2内は、前述したように曝気して
いるので、これからリターン通路3取り出される
処理液には、気泡もかなり含まれているので、こ
れによつても脱窒槽1内を厳密な嫌気状態に維持
することが難しかつた。
In particular, since the inside of the nitrification tank 2 is aerated as mentioned above, the treated liquid taken out from the return passage 3 contains a considerable amount of air bubbles. It was difficult to maintain anaerobic conditions.

そして、脱窒槽内の嫌気状態を保持する対策と
して、脱窒槽から発生する窒素ガスを用い、リタ
ーン通路の途中に設けたガス分離塔で処理液を気
ばくすることにより溶存酸素等を除去することが
考えられる。
As a measure to maintain the anaerobic state in the denitrification tank, dissolved oxygen, etc. are removed by using the nitrogen gas generated from the denitrification tank and aerating the treated liquid in a gas separation tower installed in the middle of the return passage. is possible.

しかしながら脱窒槽から発生する窒素ガスは硫
化水素等などの腐蝕性ガスを多く含むため、ガス
分離塔の防蝕等の維持管理が困難で、安価かつ寿
命の長いガス分離塔を設けることができないため
不経済であるという問題があつた。
However, since the nitrogen gas generated from the denitrification tank contains a large amount of corrosive gases such as hydrogen sulfide, it is difficult to maintain and manage the corrosion prevention of the gas separation tower, and it is not possible to install an inexpensive and long-life gas separation tower. There was an issue of economics.

この発明は、このような従来の問題点に鑑みて
なされたものであつて、その目的とするところ
は、ガス分離塔の維持管理を容易にして安価かつ
寿命の長いものを設けることができるとともに、
効率的に気ばくを行なつて脱窒槽の嫌気状態を容
易かつ確実に維持できる廃水処理装置を提供する
ことにある。
The present invention has been made in view of these conventional problems, and its purpose is to facilitate the maintenance and management of gas separation towers, and to provide inexpensive and long-life ones. ,
It is an object of the present invention to provide a wastewater treatment device that can easily and reliably maintain an anaerobic state in a denitrification tank by performing air aeration efficiently.

≪問題点を解決するための手段≫ 上記目的を達成するために、この発明の深層型
廃水処理装置は、脱窒槽と硝化槽とからなる処理
槽と、硝化槽から廃水処理液を脱窒槽に導入する
リターン通路と、該リターン通路の途中に設けた
ガス分離塔とからなり、前記処理槽に送り込んだ
廃水原液の脱窒・硝化を行う深層型廃水処理装置
において、該深層型廃水処理装置が、空気中の酸
素と窒素とを分離するガス発生装置と、該ガス発
生装置により分離された酸素ガスを前記硝化槽に
導入する酸素ガス供給路と、該ガス発生装置によ
り分離された窒素ガスを前記ガス分離塔の前流側
に供給する窒素ガス供給路とを備えることを特徴
とするものである。
<Means for Solving the Problems> In order to achieve the above object, the deep wastewater treatment device of the present invention includes a treatment tank consisting of a denitrification tank and a nitrification tank, and a wastewater treatment liquid from the nitrification tank is transferred to the denitrification tank. In a deep-layer wastewater treatment device that includes a return passage for introduction and a gas separation tower installed in the middle of the return passage, and denitrifies and nitrifies the raw wastewater sent to the treatment tank, the deep-layer wastewater treatment device , a gas generator for separating oxygen and nitrogen in the air, an oxygen gas supply path for introducing the oxygen gas separated by the gas generator into the nitrification tank, and a gas generator for introducing the nitrogen gas separated by the gas generator into the nitrification tank. A nitrogen gas supply path is provided on the upstream side of the gas separation column.

≪作用≫ 上記構成の深層型廃水処理装置によれば、ガス
発生装置により分離される窒素ガスを窒素ガス供
給路を介してガス分離塔に供給するので硝化槽で
曝気を行なうための酸素ガスを製造すべく設けた
ガス発生装置を、さらに有効に活用することがで
きる。また、ガス発生装置により分離発生する窒
素ガスは、腐蝕性ガスを含まず窒素成分が高いの
で、当該窒素ガスが供給されるガス分離塔の維持
管理を容易にするとともに、高い気ばく効果を呈
する。
<<Operation>> According to the deep-layer wastewater treatment apparatus configured as described above, the nitrogen gas separated by the gas generator is supplied to the gas separation tower via the nitrogen gas supply path, so that the oxygen gas for aeration in the nitrification tank is supplied. The gas generator provided for manufacturing can be utilized more effectively. In addition, the nitrogen gas separated and generated by the gas generator does not contain corrosive gases and has a high nitrogen content, which facilitates the maintenance and management of the gas separation tower to which the nitrogen gas is supplied, and provides a high aeration effect. .

≪実施例≫ 以下、この発明の好適な実施例について添付図
面を参照にして詳細に説明する。
<<Example>> Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the accompanying drawings.

第1図は、この発明にかかる深層型廃水処理装
置の一実施例を示している。
FIG. 1 shows an embodiment of a deep wastewater treatment apparatus according to the present invention.

同図に示す廃水処理装置は、廃水原液Aが原水
供給路10を介して、その上部空間12に供給さ
れる脱窒槽14と、この脱窒槽14と下端部で連
通した硝化槽16とからなる処理槽を備えてい
る。
The wastewater treatment apparatus shown in the figure consists of a denitrification tank 14 into which wastewater stock solution A is supplied to its upper space 12 via a raw water supply path 10, and a nitrification tank 16 that communicates with the denitrification tank 14 at its lower end. Equipped with a processing tank.

上記脱窒槽14と硝化槽16とは、ともに地下
に設けられ、その有効水深が30〜35m程度に設定
された縦形の処理槽である。
The denitrification tank 14 and the nitrification tank 16 are both vertical treatment tanks that are installed underground and have an effective water depth of about 30 to 35 m.

そして、上記脱窒槽14と硝化槽16内には、
それぞれ内部を縦方向に仕切る仕切壁18,18
aが各槽14,16の上下端から所定の間隔をお
いて設けられ、それぞれの仕切壁18,18aの
一方側には、それぞれ微生物を保持させるために
固定床型の濾材20,20aが充填されるととも
に、他方側には通路19,19aが設けられてい
る。
In the denitrification tank 14 and nitrification tank 16,
Partition walls 18, 18 that vertically partition the interior, respectively.
A is provided at a predetermined interval from the upper and lower ends of each tank 14, 16, and one side of each partition wall 18, 18a is filled with fixed bed type filter media 20, 20a to retain microorganisms, respectively. At the same time, passages 19 and 19a are provided on the other side.

上記脱窒槽14、硝化槽16内に充填される濾
材20,20aは、不織布あるいは織布などの平
面状のもの、ハニカムチユーブ、定形あるいは不
定形の充填濾材などが使用される。
The filter media 20, 20a filled in the denitrification tank 14 and the nitrification tank 16 may be flat materials such as nonwoven or woven fabrics, honeycomb tubes, fixed or irregularly shaped filter media, or the like.

また、上記脱窒槽14には、仕切壁18の他方
側に吸引口が接続された循環ポンプ22が設置さ
れ、これを駆動することにより脱窒槽14内に仕
切壁18の濾材20側に下向きの流れを創出する
とともに、濾材20の反対側の通路19内で上向
きの流れを創出する。
In addition, a circulation pump 22 with a suction port connected to the other side of the partition wall 18 is installed in the denitrification tank 14, and by driving the circulation pump 22, a downward flow is caused in the denitrification tank 14 on the filter medium 20 side of the partition wall 18. Flow is created and an upward flow is created in the passageway 19 on the opposite side of the filter media 20.

一方、硝化槽16には、その上部空間12aと
通路19aの中間部分とを連絡する配管にブロワ
24が設置され、ブロワ24を駆動すると、後述
するようにこの空間部12aに供給される酸素ガ
スが、通路19aの中間部分に送られて曝気を行
うとともに、濾材20a側で下向きの流れを創出
し、かつ、通路19a側で上向きの流れを創出す
る。
On the other hand, in the nitrification tank 16, a blower 24 is installed in a pipe connecting the upper space 12a and the middle part of the passage 19a, and when the blower 24 is driven, oxygen gas is supplied to this space 12a as described later. is sent to the middle part of the passage 19a to perform aeration, create a downward flow on the filter medium 20a side, and create an upward flow on the passage 19a side.

また、上記硝化槽16には、処理された廃水処
理液Bを排出する排出路26が接続されており、
この排出路26を介して取り出された廃水処理液
Bは、その後真空式脱気塔28と最終沈澱槽30
で処理された後に外部に放出される。
Further, a discharge path 26 for discharging the treated wastewater treatment liquid B is connected to the nitrification tank 16,
The waste water treatment liquid B taken out through this discharge path 26 is then sent to a vacuum degassing tower 28 and a final settling tank 30.
After being processed, it is released to the outside.

さらに、上記排出路26には、これから分岐し
たリターン通路32が設けられ、このリターン通
路32の他端は上記脱窒槽14に接続されてお
り、かつ、リターン通路32の途中にはガス分離
塔34が設けてある。
Further, the discharge passage 26 is provided with a return passage 32 that branches off from it, the other end of this return passage 32 is connected to the denitrification tank 14, and a gas separation tower 34 is connected to the denitrification tank 14 in the middle of the return passage 32. is provided.

そして、このガス分離塔34の前流側にはガス
発生装置36から窒素ガスが送り込まれる窒素ガ
ス供給路38が接続されている。
A nitrogen gas supply line 38 through which nitrogen gas is fed from a gas generator 36 is connected to the upstream side of the gas separation tower 34 .

上記ガス発生装置36は、吸着剤が充填された
塔内に空気を送り込み、空気中の窒素をこの吸着
剤で選択的に吸着させることにより酸素ガスを分
離製造する装置であつて、取り出された酸素ガス
は、ガス発生装置36と硝化槽16の上部空間1
2aとの間に設けられた酸素ガス供給路40を介
して硝化槽16に導入されるとともに、吸着剤に
吸着されている窒素を圧力を変えることで脱着
し、脱着された窒素ガスを上記窒素ガス供給路3
8を介して送出する。
The gas generator 36 is a device that separates and produces oxygen gas by feeding air into a tower filled with an adsorbent and selectively adsorbing nitrogen in the air with the adsorbent. Oxygen gas is supplied to the gas generator 36 and the upper space 1 of the nitrification tank 16.
Nitrogen gas is introduced into the nitrification tank 16 via an oxygen gas supply path 40 provided between the adsorbent 2a, and the nitrogen adsorbed by the adsorbent is desorbed by changing the pressure, and the desorbed nitrogen gas is Gas supply path 3
8.

以上のように構成された深層型廃水処理装置に
おいては、原水供給路10を介して廃水原液Aを
脱窒槽14内に送り込み、循環ポンプ22,ブロ
ワ24を駆動して脱窒槽14と硝化槽16内にそ
れぞれ第1図に示すような矢印方向の水流を創出
しながら廃水原液Aを処理する。
In the deep type wastewater treatment apparatus configured as described above, the wastewater raw solution A is sent into the denitrification tank 14 through the raw water supply path 10, and the circulation pump 22 and blower 24 are driven to connect the denitrification tank 14 and the nitrification tank 16. The waste water stock solution A is treated while creating water flows in the directions of the arrows as shown in FIG.

このような処理過程では、廃水原液A中に含有
されているアンモニヤ性の窒素は、硝化槽16内
でガス発生装置36からその上部空間12aに送
り込まれた酸素ガスがブロワ24によつて通路1
9aの中間部分に送られて曝気が行われるので、
排出路26に取り出される廃水処理液Bは、硝酸
性の窒素に変換され、これがリターン通路32を
介して脱窒槽14に循環されると窒素ガスとして
除去される。
In such a treatment process, the ammonia nitrogen contained in the raw wastewater solution A is removed from the passage 1 by the blower 24 when oxygen gas is sent into the upper space 12a from the gas generator 36 in the nitrification tank 16.
Since aeration is carried out by being sent to the middle part of 9a,
The wastewater treatment liquid B taken out to the discharge passage 26 is converted to nitric nitrogen, and when this is circulated to the denitrification tank 14 via the return passage 32, it is removed as nitrogen gas.

この場合、この実施例の処理装置では、リター
ン通路32の途中に設けられたガス分離塔の34
の前流側にガス発生装置36から窒素ガスが窒素
ガス供給路38を介して供給されるので、硝化槽
16からガス分離塔34内に導入された廃水処理
液Bは、分離塔34内で気ばくされ、溶存酸素が
放出されるとともに、気泡も分離される。
In this case, in the processing apparatus of this embodiment, 34 of the gas separation tower provided in the middle of the return passage 32 is
Since nitrogen gas is supplied from the gas generator 36 to the upstream side of the gas generator 36 via the nitrogen gas supply line 38, the wastewater treatment liquid B introduced from the nitrification tank 16 into the gas separation tower 34 is treated in the separation tower 34. The gas is aerated, the dissolved oxygen is released, and the air bubbles are also separated.

従つて、脱窒槽14に循環される廃水処理液b
は、溶存酸素や気泡がほとんど除去された状態に
なるので、脱窒槽14の嫌気状態に与える影響が
極めて少なくなる。
Therefore, the wastewater treatment liquid b circulated to the denitrification tank 14
Since dissolved oxygen and air bubbles are almost completely removed, the influence on the anaerobic state of the denitrification tank 14 is extremely small.

ここで、ガス発生装置により分離発生する窒素
ガスは流下水素等の腐蝕性ガスを含まず、また約
90%以上の窒素成分を含んで気ばく効果が高いの
で、効率的に処理液中の溶存酸素や気泡を除去し
て容易に脱窒槽14の嫌気状態を保持することが
できる。
Here, the nitrogen gas separated and generated by the gas generator does not contain corrosive gases such as flowing hydrogen, and approximately
Since it contains 90% or more of the nitrogen component and has a high aerobic effect, dissolved oxygen and bubbles in the treatment liquid can be efficiently removed and the anaerobic state of the denitrification tank 14 can be easily maintained.

≪発明の効果≫ 以上実施例で詳細に説明したように、この発明
にかかる深層型廃水処理装置によれば、硝化槽か
ら廃水処理液を脱窒槽に導入するリターン通路に
設けたガス分離塔の前流側に、曝気を行なうため
の酸素ガスを製造すべく設けたガス発生装置から
発生する窒素ガスを窒素ガス供給路を介して供給
するので、ガス発生装置で分離した酸素ガス及び
窒素ガスを有効に活用することができるととも
に、空気から分離した、腐蝕性ガスを含まない気
ばく効果の高い窒素ガスを使用することにより、
ガス分離塔における処理液中の溶存酸素や気泡の
除去を容易にして脱窒槽の嫌気状態を容易に保持
し、かつガス分離塔などの循環装置を安価かつ寿
命の長いものにするという各別の効果を得ること
ができる。
<<Effects of the Invention>> As explained in detail in the embodiments above, according to the deep wastewater treatment apparatus according to the present invention, the gas separation tower installed in the return passage that introduces the wastewater treatment liquid from the nitrification tank to the denitrification tank Nitrogen gas generated from a gas generator installed to produce oxygen gas for aeration is supplied to the upstream side via a nitrogen gas supply path, so the oxygen gas and nitrogen gas separated by the gas generator are By using nitrogen gas, which can be used effectively and is separated from air and does not contain corrosive gases, it has a high aeration effect.
The goal is to easily remove dissolved oxygen and bubbles from the treated liquid in the gas separation tower, maintain the anaerobic state in the denitrification tank, and make circulation equipment such as the gas separation tower inexpensive and long-lasting. effect can be obtained.

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

第1図は本発明にかかる廃水処理装置の全体
図、第2図は従来の廃水処理装置の説明図であ
る。 10……原水供給路、14……脱窒槽、16…
…硝化槽、32……リターン通路、34……ガス
分離塔、36……ガス分離装置、38……窒素ガ
ス供給路、40……酸素ガス供給路。
FIG. 1 is an overall view of a wastewater treatment device according to the present invention, and FIG. 2 is an explanatory diagram of a conventional wastewater treatment device. 10...Raw water supply channel, 14...Denitrification tank, 16...
... Nitrification tank, 32 ... Return passage, 34 ... Gas separation tower, 36 ... Gas separation device, 38 ... Nitrogen gas supply path, 40 ... Oxygen gas supply path.

Claims (1)

【特許請求の範囲】[Claims] 1 脱窒槽と硝化槽とからなる処理槽と、硝化槽
から廃水処理液を脱窒槽に導入するリターン通路
と、該リターン通路の途中に設けたガス分離塔と
からなり、前記処理槽に送り込んだ廃水原液の脱
窒・硝化を行う深層型廃水処理装置において、該
深層型廃水処理装置が、空気中の酸素と窒素とを
分離するガス発生装置と、該ガス発生装置により
分離された酸素ガスを前記硝化槽に導入する酸素
ガス供給路と、該ガス発生装置により分離された
窒素ガスを前記ガス分離塔の前流側に供給する窒
素ガス供給路とを備えることを特徴とする深層型
廃水処理装置。
1 Consisting of a treatment tank consisting of a denitrification tank and a nitrification tank, a return passage that introduces the wastewater treatment liquid from the nitrification tank to the denitrification tank, and a gas separation tower installed in the middle of the return passage, In a deep-layer wastewater treatment device that denitrifies and nitrifies wastewater concentrate, the deep-layer wastewater treatment device includes a gas generator that separates oxygen and nitrogen from the air, and a gas generator that separates oxygen gas from the gas generator. A deep wastewater treatment comprising: an oxygen gas supply line that introduces the nitrification tank; and a nitrogen gas supply line that supplies the nitrogen gas separated by the gas generator to the upstream side of the gas separation column. Device.
JP62266523A 1987-10-23 1987-10-23 Deep-type waste water processing device Granted JPH01111492A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP62266523A JPH01111492A (en) 1987-10-23 1987-10-23 Deep-type waste water processing device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP62266523A JPH01111492A (en) 1987-10-23 1987-10-23 Deep-type waste water processing device

Publications (2)

Publication Number Publication Date
JPH01111492A JPH01111492A (en) 1989-04-28
JPH0478358B2 true JPH0478358B2 (en) 1992-12-10

Family

ID=17432073

Family Applications (1)

Application Number Title Priority Date Filing Date
JP62266523A Granted JPH01111492A (en) 1987-10-23 1987-10-23 Deep-type waste water processing device

Country Status (1)

Country Link
JP (1) JPH01111492A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2519919Y2 (en) * 1990-06-15 1996-12-11 麒麟麦酒 株式会社 Septic tank
WO2022140482A1 (en) * 2020-12-21 2022-06-30 Raytheon BBN Technologies, Corp. Energy from bacteria and seabed extraction

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5929088A (en) * 1982-08-09 1984-02-16 Hitachi Plant Eng & Constr Co Ltd Treatment device for waste water
JPS61125495A (en) * 1984-11-20 1986-06-13 Hitachi Plant Eng & Constr Co Ltd Method and device for biological denitrification treatment of organic waste water

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5929088A (en) * 1982-08-09 1984-02-16 Hitachi Plant Eng & Constr Co Ltd Treatment device for waste water
JPS61125495A (en) * 1984-11-20 1986-06-13 Hitachi Plant Eng & Constr Co Ltd Method and device for biological denitrification treatment of organic waste water

Also Published As

Publication number Publication date
JPH01111492A (en) 1989-04-28

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