JPS6274490A - Method for treatment of sewage utilizing bacteria - Google Patents
Method for treatment of sewage utilizing bacteriaInfo
- Publication number
- JPS6274490A JPS6274490A JP60215841A JP21584185A JPS6274490A JP S6274490 A JPS6274490 A JP S6274490A JP 60215841 A JP60215841 A JP 60215841A JP 21584185 A JP21584185 A JP 21584185A JP S6274490 A JPS6274490 A JP S6274490A
- Authority
- JP
- Japan
- Prior art keywords
- sewage
- treatment
- magnetic force
- tank
- water
- 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.)
- Pending
Links
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
- Biological Treatment Of Waste Water (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は微生物の有機物分解作用を利用した凍原や家庭
廃水、工場廃水等の汚水処理方法に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for treating sewage such as frozen ground, domestic wastewater, industrial wastewater, etc. using the organic matter decomposition action of microorganisms.
従来より汚水処理の方法等について様々な工夫や改善が
加えられ、近年では微生物の有機物分解作用を利用した
数段階の処理工程に分けたンステムによる処理が行なわ
れるようになっている。Over the years, various innovations and improvements have been made to sewage treatment methods, and in recent years, treatment has come to be carried out using systems that are divided into several treatment steps that utilize the organic matter decomposition action of microorganisms.
すなわち、汚水が流入する浄化槽の沈澱槽では嫌気性微
生物による腐敗分解と好気性微生物による上澄液の前処
理とを行ない、土壌処理槽や曝気槽で空気を送入して曝
気と撹拌な\襖しながら好気性微生物を多量に含む活性
汚でいとlrj水とを混合、接触させる。そしてその後
、最終沈澱槽で活性汚でし・を沈澱分解させてその上澄
水を放流させるというものであった。In other words, in the sedimentation tank of the septic tank into which sewage flows, anaerobic microorganisms decompose and decompose the supernatant liquid, and aerobic microorganisms pre-treat the supernatant, and air is pumped into the soil treatment tank or aeration tank to aerate and agitate. Activated dirt containing a large amount of aerobic microorganisms and lrj water are mixed and brought into contact with each other while using a sliding door. After that, activated soil was used to precipitate and decompose the waste in the final settling tank, and the supernatant water was discharged.
しかしながら、この微生物の有機物分解作用を利用した
lす水処理方法では、汚水流入量の増大による処理能力
の7ノブには施設を拡張しなければならないし、又汚水
の水質変動等の負荷に対して微生物の対応が弱(・ため
処理水質が不安定となり、そのためtr3水流人から処
理水放流までの各部所の管理が大変であるし、この処理
水の放流による河川の汚染等水質汚濁の問題があった。However, with this water treatment method that utilizes the organic matter decomposition action of microorganisms, it is necessary to expand the facility to 7 knobs of treatment capacity due to the increase in the amount of sewage inflow, and it is also necessary to deal with loads such as changes in the quality of sewage. As a result, the quality of the treated water becomes unstable, making it difficult to manage each part from the TR3 water flow to the discharge of treated water, and the discharge of treated water causes water pollution problems such as contamination of rivers. was there.
本発明はこの従来の問題点を解決せんとなされたもので
、その目的とするところは、従来の微生物の有機物分解
作用を利用し、又近年の研究によって判明した磁力によ
る微生物の増殖作用と活性化を計ることによって汚水処
理の能力と処理水質の安定化を高めるようにした微生物
利用の汚水処理方法を提供することにあり、そのための
技術的手段として本発明では、微生物の有機物分解作用
を利用したt75水処理方法において、tr3水の処理
経路に磁力を有する素材で形成した接触材を配設し、該
磁力で微生物の増殖を促進し、有機物分解共により上質
な処理水を放流できるようにした。The present invention was made to solve this conventional problem, and its purpose is to utilize the conventional organic matter decomposition action of microorganisms, and also to increase the growth and activity of microorganisms by magnetic force, which has been discovered through recent research. The purpose of the present invention is to provide a sewage treatment method using microorganisms that improves the sewage treatment ability and stabilizes the quality of treated water by reducing the In the T75 water treatment method, a contact material made of a material with magnetic force is placed in the TR3 water treatment path, and the magnetic force promotes the growth of microorganisms, allowing for organic matter decomposition and higher quality treated water to be discharged. did.
従って、本発明では汚水の処理経路に磁力を有する素材
で形成した接触材を配設したので、微生物はこの接触材
の磁力によって増殖し、活性化されるので対応能力が倍
増し、汚水流入量の増大や水質変動等の負荷に対して十
分対処することができる。又、そのため処理水質も高度
に安定化させることができる。Therefore, in the present invention, since a contact material made of a magnetic material is provided in the wastewater treatment route, microorganisms multiply and are activated by the magnetic force of the contact material, thereby doubling the response capacity and increasing the amount of wastewater inflow. It is possible to adequately cope with loads such as increases in water and changes in water quality. Moreover, the quality of treated water can therefore be highly stabilized.
以下本発明の実施例を図面に示して説明する。 Embodiments of the present invention will be described below with reference to the drawings.
図において(1)は浄化槽、(2)は送水調整槽、(3
)は土壌処理槽である。In the figure, (1) is a septic tank, (2) is a water adjustment tank, and (3) is a septic tank.
) is a soil treatment tank.
浄化槽(1)は2室に分離され前室を1次処理室(4)
、後室を2次処理室(5)とし、この2次処理室(5)
の室内には3rn/rn〜5 m1mメノンーの網目で
筒状に形成された磁力を有する接触材(6)を多数直立
させた状態に取付け、散気管(7)で汚水の曝気と撹拌
をする。送水調整槽(2)は浄化槽(1)からの不規則
な流入を調整し、エアリフトポンプ(8)によって定量
的に土壌処理槽(3)に送水している。The septic tank (1) is separated into two chambers, with the front chamber serving as the primary treatment chamber (4).
, the rear chamber is a secondary processing chamber (5), and this secondary processing chamber (5)
In the room, a large number of contact materials (6) with magnetic force formed in a cylindrical shape with a mesh of 3rn/rn to 5 m1m are installed in an upright position, and the wastewater is aerated and stirred with an aeration pipe (7). . The water supply adjustment tank (2) regulates irregular inflow from the septic tank (1), and quantitatively supplies water to the soil treatment tank (3) using an air lift pump (8).
前記土壌処理槽(3)は、室内下面から上方に向かって
栗石(9)、割り石(10、砂止めマy ト(If)、
磁カマブト(1り、川砂(13、磁気マノ)(+4、真
砂土(l→の順に堆積させている。又栗石(9)の中程
には散気管(lflを設は汚水の曝気とマント類の目づ
まり防止とを行なっている。The soil treatment tank (3) has a chestnut stone (9), a split stone (10), a sand stopper (If),
Magikamabuto (1ri), river sand (13, magnetic mano) (+4), Masago soil (l → deposited in the order of This prevents clogging.
前記磁気づノド(l望および(lΦは3m1m〜5 m
1mメツ/−の網目状で磁気を有する素材により形成さ
れたマットであり、前記磁気を有する接触材(6)RI
H束密度150ガウス程度のものを使用している。The magnetic nose (lΦ and (lΦ is 3m1m~5m
It is a mat formed of a magnetic material with a mesh size of 1 m/-, and the magnetic contact material (6) RI
The H flux density is about 150 Gauss.
本実施例の7ステムは以上の様に溝数され、1次処理室
(4)に流入した凍原はここで固形物が沈澱腐敗し上澄
液が次の2次処理室(5)へ流入する。The seven stems of this example have the number of grooves as described above, and the frozen ground that flows into the primary treatment chamber (4) is where the solid matter settles and rots, and the supernatant liquid flows into the next secondary treatment chamber (5). do.
2次処理室(5)へ流入した汚水は散気管(7)で曝気
され、かつ撹拌されるが、このとぎ微生物も同時に撹拌
され、接触材(6)と十分に接触し、その磁力を受けて
増殖する。又微生物は磁力によって活性化し、汚水の有
機物を活発に分解する。そしてここで次々と分解された
汚水の上澄液が送水調整槽(2)に流入し、これがエア
リフトポンプ(8)によって次の土壌処理槽(3)に定
量的に流入する。この土壌処理槽(3)では川砂(13
を磁気マツ) (laおよび(14です/ドイノチした
状態にして設け、このために上昇水流が満偏なく広がり
、又流速の遅くなった部分で上昇水流中の微生物が磁力
を受けるように設けている。又散気管(10による曝気
と相まって微生物は増殖し、かつ活性化されて汚水の有
機物分解作用が急激に行なわれる。そしてここでの上澄
液は従来処理水の1/1a以下のB、O,Dの水質まで
浄化できた。The sewage that has flowed into the secondary treatment chamber (5) is aerated and stirred by the aeration pipe (7), and the microorganisms are also stirred at the same time, making sufficient contact with the contact material (6) and receiving its magnetic force. and multiply. In addition, microorganisms are activated by magnetic force and actively decompose organic matter in wastewater. Then, the supernatant liquid of the decomposed wastewater flows into the water supply adjustment tank (2), and quantitatively flows into the next soil treatment tank (3) by the air lift pump (8). In this soil treatment tank (3), river sand (13
(magnetic pine) (la and (14)/ It is set in a state of being tilted, so that the rising water flow spreads evenly, and the microorganisms in the rising water flow receive magnetic force in the part where the flow velocity is slow. In addition, in combination with the aeration provided by the aeration tube (10), microorganisms proliferate and are activated, resulting in rapid decomposition of organic matter in wastewater. , O, D water quality.
以上示すように本実施例によれば汚水の処理経路である
浄化槽(1)に筒状に形成した磁力を有する接触材を設
け、かつ土壌処理槽(3)の川砂+13を磁気マット(
lilpおよび(1,0でサンドイッチ状に設けたので
微生物は増殖と活性化に要する磁力を十分に受けること
ができ、有機物の分解を十分に行なうことができる。こ
のため、汚水流入量の増大や水質変動等の負荷変動に対
して施設を大型化しないで十分対処することができる。As shown above, according to this embodiment, a cylindrical contact material having magnetic force is provided in the septic tank (1) which is the wastewater treatment route, and the river sand +13 in the soil treatment tank (3) is covered with a magnetic mat (
Since the lilp and (1,0) are provided in a sandwich configuration, microorganisms can receive sufficient magnetic force for growth and activation, and can fully decompose organic matter. Load fluctuations such as changes in water quality can be adequately dealt with without increasing the size of the facility.
又、従来のシステムによるものが放流水のB、O,D濃
度10〜30ppmと大きくかつ不安定で変動が大きい
のに対し、今回実施したシステムではB、O,D濃度が
3 ppm以下となって大巾に改善されたことが判明し
た。従って従来システムで行なってきた微生物の培養や
システムの調整、管理に要する人員を大巾に削減するこ
とができる。In addition, in contrast to the conventional system, where the B, O, and D concentrations in the effluent water are large, unstable, and fluctuate at 10 to 30 ppm, the B, O, and D concentrations in the system implemented this time are 3 ppm or less. It turned out that there was a huge improvement. Therefore, the number of personnel required for culturing microorganisms and adjusting and managing the system, which have been performed in conventional systems, can be greatly reduced.
以上本発明の実施例を図面に示して説明したが、本発明
の具体的な方法、溝数はこの実施例に限定されたもので
はなく、本発明の要旨を逸脱しない範囲の設計変更等が
あっても本発明の技術的範囲に含まれる。Although the embodiments of the present invention have been described above with reference to the drawings, the specific method and number of grooves of the present invention are not limited to these embodiments, and design changes may be made without departing from the gist of the present invention. Even if there is, it is within the technical scope of the present invention.
例えば本実施例では磁気を有する素材の磁束密度が15
0ガウス程度のものを使用するとしたが、これに限らず
磁束密度は100ガウスから800ガウス程度のものか
ら最適なものを選定できるものである。又、接触材の形
状や取付位置等も実施例に限定されるものではない。For example, in this example, the magnetic flux density of the magnetic material is 15
Although it is assumed that a magnetic flux density of about 0 Gauss is used, the optimum magnetic flux density can be selected from those with a magnetic flux density of about 100 Gauss to 800 Gauss. Furthermore, the shape and mounting position of the contact material are not limited to the embodiments.
又、浄化槽の内部を2室に分離したが、これに限らずそ
れぞれ独立した沈澱槽や曝気槽として設けてもよい。又
土壌処理槽は散気管で送気したが、これに限らず散気管
の取付等は任1行に決定できるものである。Further, although the inside of the septic tank is divided into two chambers, the present invention is not limited to this, and each chamber may be provided as an independent sedimentation tank or an aeration tank. In addition, air was supplied to the soil treatment tank using an aeration pipe, but the installation of the aeration pipe is not limited to this, and each bank can decide on the installation of the aeration pipe.
又、実施例では凍原処理のシステムで説明したが、これ
に限らず、家庭や工場等の雑廃水の処理にも適用できる
。Furthermore, although the embodiment has been described using a frozen ground treatment system, the present invention is not limited to this, and can also be applied to the treatment of miscellaneous wastewater from homes, factories, etc.
以上説明したように本発明によれば接触材やマットに磁
力を有する素材を使用したので汚水処理をする微生物の
増殖を促進し、有機物分解作用を活性化し、負荷の変動
があっても処理水質を常に安定化させ、かつ上質な処理
水とすることかできる。As explained above, according to the present invention, since magnetic materials are used for the contact material and mat, it promotes the growth of microorganisms that treat sewage, activates organic matter decomposition, and improves the quality of treated water even when the load fluctuates. It is possible to constantly stabilize the water and produce high-quality treated water.
又、これによって処理水放流による河川の汚染をなくし
、水質力面による環境汚染を防止することかできる。In addition, this eliminates river pollution caused by discharge of treated water and prevents environmental pollution caused by water quality.
又、作業人員等が大巾に削減できるのでランニングコス
トを低減させることができる。Furthermore, since the number of workers etc. can be greatly reduced, running costs can be reduced.
図は本発明実施例の汚水処理システムを示す説明図であ
る。
(6):接触材
(1り:磁気マント(接触材)The figure is an explanatory diagram showing a sewage treatment system according to an embodiment of the present invention. (6): Contact material (1: Magnetic cloak (contact material)
Claims (1)
おいて、汚水の処理経路に磁力を有する素材で形成した
接触材を配設し、該磁力で微生物の増殖を促進し、有機
物分解作用を活性化し、かつ処理水質を安定化させると
共により上質な処理水を放流できるようにしたことを特
徴とする微生物利用汚水処理方法。1) In a wastewater treatment method that utilizes the organic matter decomposition action of microorganisms, a contact material made of a magnetic material is placed in the wastewater treatment path, and the magnetic force promotes the growth of microorganisms and activates the organic matter decomposition action. A sewage treatment method using microorganisms, which is characterized in that the quality of the treated water is stabilized and treated water of higher quality can be discharged.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60215841A JPS6274490A (en) | 1985-09-27 | 1985-09-27 | Method for treatment of sewage utilizing bacteria |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP60215841A JPS6274490A (en) | 1985-09-27 | 1985-09-27 | Method for treatment of sewage utilizing bacteria |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS6274490A true JPS6274490A (en) | 1987-04-06 |
Family
ID=16679150
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP60215841A Pending JPS6274490A (en) | 1985-09-27 | 1985-09-27 | Method for treatment of sewage utilizing bacteria |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS6274490A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0295495A (en) * | 1988-09-29 | 1990-04-06 | Ryuichi Kamogawa | Method of using excreta treatment accelerating agent |
Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5473461A (en) * | 1977-11-24 | 1979-06-12 | Inoue Japax Res Inc | Improved device for treating water |
-
1985
- 1985-09-27 JP JP60215841A patent/JPS6274490A/en active Pending
Patent Citations (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5473461A (en) * | 1977-11-24 | 1979-06-12 | Inoue Japax Res Inc | Improved device for treating water |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0295495A (en) * | 1988-09-29 | 1990-04-06 | Ryuichi Kamogawa | Method of using excreta treatment accelerating agent |
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