JPS641198B2 - - Google Patents
Info
- Publication number
- JPS641198B2 JPS641198B2 JP13572585A JP13572585A JPS641198B2 JP S641198 B2 JPS641198 B2 JP S641198B2 JP 13572585 A JP13572585 A JP 13572585A JP 13572585 A JP13572585 A JP 13572585A JP S641198 B2 JPS641198 B2 JP S641198B2
- Authority
- JP
- Japan
- Prior art keywords
- wastewater
- tank
- aeration
- channel
- 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.)
- Expired
Links
- 239000002351 wastewater Substances 0.000 claims description 56
- 238000005273 aeration Methods 0.000 claims description 33
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 28
- 230000001105 regulatory effect Effects 0.000 claims description 11
- 238000004065 wastewater treatment Methods 0.000 claims description 10
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 8
- 229910052760 oxygen Inorganic materials 0.000 description 8
- 239000001301 oxygen Substances 0.000 description 8
- 238000000034 method Methods 0.000 description 6
- 230000003647 oxidation Effects 0.000 description 6
- 238000007254 oxidation reaction Methods 0.000 description 6
- 238000000746 purification Methods 0.000 description 4
- 230000005484 gravity Effects 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 230000003068 static effect Effects 0.000 description 2
- 238000013459 approach Methods 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 230000008719 thickening Effects 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Activated Sludge Processes (AREA)
Description
【発明の詳細な説明】
(産業上の利用分野)
本願は汚水及び産業廃水等の廃水処理方法及び
その装置に係る発明である。DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present application relates to a method and apparatus for treating wastewater such as sewage and industrial wastewater.
(従来の技術とその問題点)
従来の廃水処理装置は長時間曝気方式、酸化溝
堅型方式、酸化溝横型方式、回転板接触方式、土
壌式、接触曝気方式等のものがある。(Prior art and its problems) Conventional wastewater treatment devices include long-time aeration systems, oxidation groove vertical systems, oxidation groove horizontal systems, rotary plate contact systems, soil systems, and contact aeration systems.
しかし、上記長時間曝気方式、接触曝気方式及
び土壌式は、いずれも曝気槽を必要とするため設
備が大がかりとなつて設備費がかさみ、長時間曝
気方式、接触曝気方式は廃水移送用のポンプ及び
曝気用のブロー等を必要とするため電力消費量が
大となる問題があつた。 However, the long-time aeration method, contact aeration method, and soil method all require an aeration tank, which increases equipment costs. There was also the problem that power consumption was high because it required a blower for aeration, etc.
また、酸化溝堅型方式、酸化溝横型方式及び回
転板接触方式も夫々酸化溝及び回転板接触槽等を
必要とするため前記と同様設備が大がかりとな
り、さらにBOD負荷の少ない時は過曝気となる
ため間欠運転を余儀なくされ、運転効率が悪いば
かりでなく、消費電力が大となり無駄なエネルギ
ーを使用するという問題があつた。 In addition, the oxidation groove rigid type, oxidation groove horizontal type, and rotary plate contact type require oxidation grooves and rotary plate contact tanks, respectively, so the equipment is large-scale, and when the BOD load is low, over-aeration may occur. This necessitated intermittent operation, which not only resulted in poor operating efficiency, but also increased power consumption and wasted energy.
(発明が解決しようとする技術的課題)
以上の問題を解決しようとする本発明の技術的
課題は、廃水を能率よく処理すること、廃水処理
装置の設備を縮少することにより設備費の節減を
図り、さらに効率良い運転で廃水処理能率を上げ
ることにより消費電力を節約することである。(Technical Problems to be Solved by the Invention) The technical problems of the present invention to solve the above problems are to efficiently treat wastewater and reduce equipment costs by reducing the equipment of wastewater treatment equipment. The aim is to save power consumption by increasing wastewater treatment efficiency through more efficient operation.
(技術的課題を達成するための技術的手段)
以上の技術的課題を達成するための技術的手段
は、第1発明において調整槽に導入した廃水を下
流側が高く傾斜配設された傾斜送水路及び空気混
合コンベアーよりなる曝気送水路で上昇運搬しな
がら空気混合して曝気し、この曝気された廃水を
調整槽に返還し、この調整槽内の廃水を再び上記
同様に繰返しながら曝気浄化せしめ、その曝気浄
化された処理水を沈澱槽に移流せしめることであ
る。(Technical means for achieving the technical problem) The technical means for achieving the above-mentioned technical problem is that in the first invention, the wastewater introduced into the regulating tank is transported through an inclined water channel whose downstream side is arranged at a high slope. The wastewater is mixed with air and aerated while being conveyed upward in an aeration channel consisting of an air mixing conveyor, and the aerated wastewater is returned to the adjustment tank, and the wastewater in the adjustment tank is purified by aeration while repeating the above-mentioned process again. The process is to advect the aerated and purified treated water to a settling tank.
第2発明において廃水が導入される調整槽から
その調整槽の下流側に設けられる沈澱槽にわたつ
て、廃水用の傾斜送水路及び空気混合コンベアー
よりなる曝気送水路を下流側を高く傾斜配設せし
め、該曝気送水路の下流側端部から調整槽にわた
つて廃水循環路を設けたことである。 In the second invention, an aeration feed channel consisting of an inclined feed channel for wastewater and an air mixing conveyor is arranged with a high slope on the downstream side, extending from a regulating tank into which wastewater is introduced to a settling tank provided on the downstream side of the regulating tank. First, a wastewater circulation path is provided from the downstream end of the aeration channel to the adjustment tank.
(作 用)
調整槽内の廃水は、曝気送水路による上昇運搬
中に空気が混合されて曝気されるのみならず、曝
気送水路の空気混合コンベアーによる上昇流と、
重力による下降流とが激しくぶつかり合つて曝気
効率が促進される。そして、このような曝気した
廃水を調整槽に返還し、再び上記と同様に繰返し
循還せしめながら曝気浄化することによつて、浄
化効率が向上し、相当高度に浄化された処理水が
沈澱槽に移流される。(Function) The wastewater in the adjustment tank is not only mixed with air and aerated while being transported upward by the aeration channel, but also by the upward flow caused by the air mixing conveyor in the aeration channel.
Aeration efficiency is promoted by violently colliding with the downward flow due to gravity. By returning this aerated wastewater to the adjustment tank and purifying it with aeration while repeatedly circulating it in the same manner as above, the purification efficiency is improved, and the treated water that has been purified to a fairly high level is sent to the settling tank. is advected to
(発明の効果)
本発明は、叙上の如き構成としたことによつて
以下の効果を発揮する。(Effects of the Invention) The present invention exhibits the following effects by having the configuration as described above.
調整槽内の廃水は、曝気送水路による上昇運
搬中に空気が混合されて曝気されるのみなら
ず、曝気送水路による上昇流と、重力による下
降流とが激しくぶつかり合つて曝気効率が促進
される。従つて、曝気送水路による上昇運搬中
の廃水は、圧縮空気によつて加圧浄化せずと
も、溶存酸素濃度(DO)が飽和値近くまで速
やかに上昇して浄化される。 The wastewater in the adjustment tank is not only mixed with air and aerated while being transported upward by the aeration channel, but also the upward flow by the aeration channel and the downward flow due to gravity collide violently, promoting aeration efficiency. Ru. Therefore, the dissolved oxygen concentration (DO) of the wastewater being transported upward through the aeration channel quickly rises to near the saturation value and is purified without being pressurized and purified using compressed air.
上記の如く曝気した廃水を調整槽に返還し、
再び上記と同様に繰返し循還せしめながら曝気
浄化することによつて、浄化効率が向上し、相
当高度に浄化された処理水を沈澱槽に移流せし
め得る。従つて、沈澱槽の負担を軽減せしめる
ことができ、高度に浄化された上澄水(浄化
水)を能率よく放流することができる。 Return the aerated wastewater as described above to the adjustment tank,
By carrying out aeration purification while repeatedly circulating the water in the same manner as above, the purification efficiency is improved, and the treated water that has been purified to a fairly high degree can be advected to the settling tank. Therefore, the load on the sedimentation tank can be reduced, and highly purified supernatant water (purified water) can be efficiently discharged.
曝気槽、酸化槽及びブロー装置等の設備を必
要としないため廃水処理装置の設備を縮少する
ことができるので設備費の節減を図ることがで
きる。 Since equipment such as an aeration tank, an oxidation tank, and a blowing device is not required, the equipment of the wastewater treatment equipment can be reduced, and the equipment cost can be reduced.
前記曝気効率の向上、浄化効率の向上などに
より、効率良い運転で廃水処理能率を増進せし
め得て、消費電力の節約を図り得る。 By improving the aeration efficiency and purification efficiency, wastewater treatment efficiency can be increased through efficient operation, and power consumption can be saved.
(実施例) 本発明の一実施例を図面により説明する。(Example) An embodiment of the present invention will be described with reference to the drawings.
本発明の廃水処理装置Aは調整槽1、沈澱槽2
及び曝気送水路3により構成される。 The wastewater treatment device A of the present invention has a regulating tank 1 and a settling tank 2.
and an aeration waterway 3.
調整槽1は廃水貯水槽4と該貯水槽4の周囲に
設けた廃水路5とからなり、隣接する流入廃水処
理室6と移送管7により連結され該処理室6に流
入した廃水は移送管7の端部に設けたポンプ8に
より貯水槽4内に移送される。 The regulating tank 1 consists of a wastewater storage tank 4 and a wastewater channel 5 provided around the water storage tank 4, and is connected to an adjacent inflow wastewater treatment chamber 6 by a transfer pipe 7, so that the wastewater flowing into the treatment chamber 6 is passed through the transfer pipe. The water is transferred into the water tank 4 by a pump 8 provided at the end of the water tank 7 .
貯水槽4内には貯水槽水位計9及び該水位計9
と電気的に接続された放出電動弁10が設けられ
ており、前記処理室6から移送された廃水が一定
水位に達すると前記放出電動弁10が開動して廃
水路5内に放出される。 A water tank water level gauge 9 and a water level gauge 9 are installed in the water tank 4.
A discharge motor operated valve 10 is provided which is electrically connected to the wastewater discharge valve 10, and when the wastewater transferred from the treatment chamber 6 reaches a certain water level, the discharge motorized valve 10 opens and is discharged into the waste water channel 5.
廃水路5は曝気送水路3を介して沈澱槽2と連
絡され、廃水路5内の廃水を沈澱槽2内に移送す
る。 The waste water channel 5 is connected to the settling tank 2 via the aeration channel 3, and the waste water in the waste water channel 5 is transferred into the settling tank 2.
また廃水路5内には、後述するコントローラー
11と電気的に接続されて廃水中の酸素の溶存濃
度(DO)を測定するためのDOセンサー12及
び廃水路水位計13が設けられており貯水槽4か
ら放出された廃水が一定水位に達すると曝気送水
路3により移送される。 Furthermore, in the waste water channel 5, a DO sensor 12 and a waste water level gauge 13 are provided which are electrically connected to a controller 11 to be described later and measure the dissolved concentration of oxygen (DO) in the waste water. When the wastewater discharged from 4 reaches a certain water level, it is transferred by the aeration water channel 3.
曝気送水路3は貯水槽4を挟む形で廃水路5の
両側に夫々傾斜配設され、その下流側端部でこれ
らが合流され、沈澱槽2に連絡される。 The aeration channels 3 are inclinedly arranged on both sides of the waste water channel 5 with the water storage tank 4 in between, and are joined at the downstream end thereof and connected to the sedimentation tank 2.
前記合流部14には曝気送水路3から分岐して
調整槽1の廃水路5に連絡する廃水循環路15が
設けられると共に、該合流部14にエアーエゼク
ター部17が形成される。また該合流部14より
上流側の曝気送水路3を、下流側端部を約30゜〜
35゜高くして傾斜配設せしめることにより、傾斜
送水路3aを形成すると共に、該傾斜送水路3a
内に空気混合コンベアー16を傾斜装備する。 The confluence section 14 is provided with a waste water circulation path 15 that branches off from the aeration channel 3 and communicates with the waste water channel 5 of the regulating tank 1, and an air ejector section 17 is formed in the confluence section 14. In addition, the aeration channel 3 on the upstream side of the confluence part 14 is set at an angle of about 30° to the downstream end.
By increasing the height by 35 degrees and slanting the arrangement, an inclined water supply channel 3a is formed, and the inclined water supply channel 3a
An air mixing conveyor 16 is tilted inside.
空気混合コンベアー16は全長にわたつてスパ
イラルフイレ16aを有し、傾斜送水路3aの流
入側及び流出側の両側部に設けた固定具16bに
より傾斜送水路3a内に傾斜装備され、コントロ
ーラー11と電気的に接続されたモーター18に
より回転して廃水路5内の廃水を上昇運搬し、こ
の上昇運搬中の廃水に空気を混合せしめて曝気す
る。上昇運搬されつつある廃水は、その上昇流
と、重力による下降流とが激しくぶつかり合つて
曝気効率が促進される。 The air mixing conveyor 16 has a spiral fillet 16a over its entire length, is installed in an inclined manner within the inclined water supply channel 3a by means of fixtures 16b provided on both sides of the inflow and outflow sides of the inclined water supply channel 3a, and is connected to the controller 11. It is rotated by an electrically connected motor 18 to upwardly transport the wastewater in the wastewater channel 5, and aerates the wastewater being mixed with air while being transported upwardly. As wastewater is being transported upward, its upward flow and downward flow due to gravity collide violently, promoting aeration efficiency.
廃水循環路15は調整槽1の廃水路5から上昇
運搬された廃水を再び調整槽1の廃水路5に返送
するためのものであり、前記エアーエゼクター部
17及びその中途部に空気ミキサー部19が設け
られ、エアーエゼクター部17で廃水中に吸入さ
れた空気を空気ミキサー部19でミキシングして
酸素の溶存量を高める。 The wastewater circulation path 15 is for returning the wastewater that has been raised and transported from the wastewater channel 5 of the regulating tank 1 to the wastewater channel 5 of the regulating tank 1, and includes the air ejector section 17 and an air mixer section 19 in the middle thereof. is provided, and the air sucked into the wastewater by the air ejector part 17 is mixed by the air mixer part 19 to increase the amount of dissolved oxygen.
エアーエゼクター部17は前記コントローラー
11と電気的に接続した電動ダンパー20aを有
するエアーエゼクター20が設けられ、前記傾斜
送水路3aの空気混合コンベアー16で達成出来
なかつた酸素の溶存量に応じて電動ダンパー20
aが自動調整されて空気が吸入される。 The air ejector section 17 is provided with an air ejector 20 having an electric damper 20a electrically connected to the controller 11. 20
a is automatically adjusted and air is inhaled.
コントローラー11は、溶存酸素濃度計21、
電子式調節計22、モーターポテンシヨメーター
23、静止型周波数変換器24とよりなり、DO
センサー12、電動モーター18及び電動ダンパ
ー20が夫々電気的に作動される。 The controller 11 includes a dissolved oxygen concentration meter 21,
It consists of an electronic controller 22, a motor potentiometer 23, and a static frequency converter 24.
Sensor 12, electric motor 18, and electric damper 20 are each electrically operated.
而して、調整槽1における貯水槽4内に移送さ
れた廃水は、高水位に達すると、貯水槽4の周囲
に設けた廃水路5に流入され、該廃水路5の上限
水位に達すると傾斜送水路3aの空気混合コンベ
アー16が電動モーター18の駆動により起動す
る。 When the wastewater transferred to the water storage tank 4 in the adjustment tank 1 reaches a high water level, it flows into the wastewater channel 5 provided around the water storage tank 4, and when the wastewater reaches the upper limit water level of the wastewater channel 5. The air mixing conveyor 16 of the inclined waterway 3a is started by driving the electric motor 18.
このとき、廃水路5内の廃水の酸素溶存濃度
DOがDOセンサー12により測定され、その値
がコントローラー11の溶存酸素濃度計21によ
つて表示される。 At this time, the dissolved oxygen concentration of the wastewater in the wastewater channel 5
DO is measured by the DO sensor 12, and the value is displayed by the dissolved oxygen concentration meter 21 of the controller 11.
そして該DO値と電子調節計22であらかじめ
設定されたDO値との偏差に応じて、前記空気混
合コンベアー16の電動モーター18の回転数が
モーターポテンシヨメーター23により制御され
る。しかし、前記電動モーター18の回転数が最
大となつてもDO値が前記設定値に達しない場合
は、静止型周波数変換器24により電動ダンパー
20aの開閉が自動調整されて空気が流入され、
それが空気ミキサー部19でミキシングされ、空
気中の酸素が廃水中に混合されてDO値が高めら
れる。 The rotation speed of the electric motor 18 of the air mixing conveyor 16 is controlled by the motor potentiometer 23 according to the deviation between the DO value and the DO value preset by the electronic controller 22. However, if the DO value does not reach the set value even if the rotational speed of the electric motor 18 reaches the maximum, the static frequency converter 24 automatically adjusts the opening and closing of the electric damper 20a to allow air to flow in.
This is mixed in the air mixer section 19, oxygen in the air is mixed into the wastewater, and the DO value is increased.
これでも不充分なときは、電動ダンパー20a
がさらに自動調整され、設定されたDO値に達す
るまで調整される。そして、DO値が設定値に近
ずくに従つて電動モーター18の回転数は減少す
る。 If this is still insufficient, use the electric damper 20a.
is further automatically adjusted until the set DO value is reached. Then, as the DO value approaches the set value, the rotation speed of the electric motor 18 decreases.
上記の様に空気ミキサー部19で空気をミキシ
ングされた廃水は、前記調整槽1における廃水路
5内に返還され、このような循環を繰り返すこと
によりBOD(生物化学的酸素要求量)の除去目的
を達する。 The wastewater mixed with air in the air mixer section 19 as described above is returned to the waste water channel 5 in the adjustment tank 1, and by repeating such circulation, the purpose is to remove BOD (biochemical oxygen demand). reach.
上記BODの除去目的を達した処理水は、沈澱
槽2内に移流される。 The treated water that has achieved the purpose of removing BOD is advected into the settling tank 2.
また、該沈澱槽2内に移流される処理水は、流
入廃水量と同等であり、沈澱槽2内の余剰汚泥は
屋外貯溜濃縮槽(図示せず)に移送され、返送汚
泥は廃水路5に返送する。 In addition, the treated water advected into the settling tank 2 is equivalent to the amount of inflowing wastewater, the excess sludge in the settling tank 2 is transferred to an outdoor storage thickening tank (not shown), and the returned sludge is transferred to the waste water channel 5. send it back to
第1図は本発明の縦断正面図、第2図は一部切
欠平面図である。
尚、図中 A…廃水処理装置、1…調整槽、2
…沈澱槽、3…曝気送水路、3a…傾斜送水路、
16…空気混合コンベアー。
FIG. 1 is a longitudinal sectional front view of the present invention, and FIG. 2 is a partially cutaway plan view. In addition, in the figure A...wastewater treatment equipment, 1...adjustment tank, 2
... Sedimentation tank, 3... Aeration waterway, 3a... Inclined waterway,
16...Air mixing conveyor.
Claims (1)
設された傾斜送水路及び空気混合コンベアーより
なる曝気送水路で上昇運搬しながら空気混合して
曝気し、この曝気された廃水を調整槽に返還し、
この調整槽内の廃水を再び上記同様に繰返し循環
しながら曝気浄化せしめ、その曝気浄化された処
理水を沈澱槽に移流せしめる廃水処理方法。 2 廃水が導入される調整槽からその調整槽の下
流側に設けられる沈澱槽にわたつて、廃水用の傾
斜送水路及び空気混合コンベアーよりなる曝気送
水路を下流側を高く傾斜配設せしめ、該曝気送水
路の下流側端部から調整槽にわたつて廃水循環路
を設けた廃水処理装置。[Scope of Claims] 1. Wastewater introduced into a regulating tank is mixed with air and aerated while being conveyed upward in an aeration channel consisting of an inclined water channel whose downstream side is highly inclined and an air mixing conveyor. Return wastewater to the adjustment tank,
A wastewater treatment method in which the wastewater in this adjustment tank is repeatedly circulated in the same manner as described above to be aerated and purified, and the aerated and purified treated water is transferred to a settling tank. 2. An aeration channel consisting of an inclined waste water channel and an air mixing conveyor is arranged with a high slope on the downstream side, extending from the regulating tank into which wastewater is introduced to the settling tank provided downstream of the regulating tank. A wastewater treatment device with a wastewater circulation path extending from the downstream end of the aeration channel to the adjustment tank.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60135725A JPS61293593A (en) | 1985-06-20 | 1985-06-20 | Method and apparatus for treating waste water |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60135725A JPS61293593A (en) | 1985-06-20 | 1985-06-20 | Method and apparatus for treating waste water |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61293593A JPS61293593A (en) | 1986-12-24 |
| JPS641198B2 true JPS641198B2 (en) | 1989-01-10 |
Family
ID=15158420
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60135725A Granted JPS61293593A (en) | 1985-06-20 | 1985-06-20 | Method and apparatus for treating waste water |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61293593A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0326696U (en) * | 1989-07-27 | 1991-03-18 |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6214997A (en) * | 1985-07-13 | 1987-01-23 | Hokkaido Kankyo Seibi Kogyo Kk | Apparatus for treating waste water |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4253775A (en) * | 1979-06-29 | 1981-03-03 | Ibm Corporation | Apparatus for re-inking a ribbon in a thermal transfer printing system |
-
1985
- 1985-06-20 JP JP60135725A patent/JPS61293593A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0326696U (en) * | 1989-07-27 | 1991-03-18 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61293593A (en) | 1986-12-24 |
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