JPS5855996Y2 - organic sewage treatment equipment - Google Patents

organic sewage treatment equipment

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Publication number
JPS5855996Y2
JPS5855996Y2 JP1980102581U JP10258180U JPS5855996Y2 JP S5855996 Y2 JPS5855996 Y2 JP S5855996Y2 JP 1980102581 U JP1980102581 U JP 1980102581U JP 10258180 U JP10258180 U JP 10258180U JP S5855996 Y2 JPS5855996 Y2 JP S5855996Y2
Authority
JP
Japan
Prior art keywords
filter media
filter
wastewater
filter bed
sewage treatment
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
JP1980102581U
Other languages
Japanese (ja)
Other versions
JPS5725795U (en
Inventor
和彦 村上
隆 大屋
Original Assignee
株式会社 大管工業
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Filing date
Publication date
Application filed by 株式会社 大管工業 filed Critical 株式会社 大管工業
Priority to JP1980102581U priority Critical patent/JPS5855996Y2/en
Publication of JPS5725795U publication Critical patent/JPS5725795U/ja
Application granted granted Critical
Publication of JPS5855996Y2 publication Critical patent/JPS5855996Y2/en
Expired legal-status Critical Current

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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

Description

【考案の詳細な説明】 本考案は汚水処理装置、詳しくは、好気性微生物の着性
しうる比表面積の大なる濾材を、充填固定された槽内濾
床に、充分な溶存酸素を含ませた有機性汚水を反復して
循環させながら、濾材に着生する好気性生物により生物
化学的に酸化分解しつつ濾過し、浄化処理をする方式の
有機性汚水処理装置に関する。
[Detailed description of the invention] The present invention is a sewage treatment system, specifically, a filter bed in a tank filled and fixed with a filter medium having a large specific surface area to which aerobic microorganisms can attach, is used to contain sufficient dissolved oxygen. The present invention relates to an organic sewage treatment system in which organic sewage is repeatedly circulated, filtered and purified while being biochemically oxidized and decomposed by aerobic organisms that grow on the filter medium.

上記方式の有機性汚水処理装置は、従来の散水濾床法、
長時間ばつき法、標準活性汚泥法等と異なり、接触ばつ
き法の一種で二次処理された汚水を次後濾床の新配故に
より更に高次処理する場合に適用して極めて有用なる処
理装置である。
The organic sewage treatment equipment of the above method uses the conventional trickling filter method,
Unlike the long-time bombardment method, standard activated sludge method, etc., this method is a type of contact bombardment method and is extremely useful when secondary-treated sewage is subjected to higher-level treatment by installing a new filter bed. It is a processing device.

従来法の処理装置では、高度の浄化性能を有しているが
、有機性汚水に含まれる窒素関係の処理において、アン
モニア性窒素及びアルブミノイド性窒素を亜硝酸性窒素
或は硝酸性窒素にまで酸化できるが、それ以上の窒素除
去つまり窒素ガスとして脱窒するまでには至らず、汚水
中からの窒素分の除去が困難である点及び活性汚泥の膨
化による汚泥の流出が認められ、また剥離汚泥が微細な
難沈降性のピンフロックとして処理水中に流出し易い欠
点があり、尚装置の管理上に於ても余剰汚泥の発生量が
多く、問題があった。
Conventional treatment equipment has a high degree of purification performance, but in the treatment of nitrogen contained in organic wastewater, ammonia nitrogen and albuminoid nitrogen are oxidized to nitrite nitrogen or nitrate nitrogen. However, further nitrogen removal, that is, denitrification as nitrogen gas, has not been achieved, and it has been observed that it is difficult to remove nitrogen from sewage, and that sludge flows out due to swelling of activated sludge. The disadvantage is that the sludge easily flows out into the treated water as fine pin flocs that do not easily settle, and there is also a problem in the management of the equipment, as a large amount of surplus sludge is generated.

そして上記の如く剥離した汚泥が微細な難沈降性ピンフ
ロックとして、処理水中に流出した場合、処理水の水質
の劣化を招くという問題を生じる。
If the sludge exfoliated as described above flows into the treated water as fine, non-settling pin flocs, a problem arises in that the quality of the treated water deteriorates.

本考案の目的は、好気性微生物の着生し得る比表面積が
大なる濾材が充填固定された濾床に、充分な溶存酸素を
含ませた有機性汚水を反復して循環させながら、濾材に
着生する好気性微生物により生物化学的に酸化分解しつ
つ濾過し浄化処理する方式の汚水処理装置として、汚水
が濾材に十分接触して該濾材に着生した微生物により十
分分解され、汚水中の窒素骨除去が高度に行われ、処理
水中への浮遊物流出が殆ど防止され、更に余剰汚泥の発
生が少ない汚水処理装置を提供することにある。
The purpose of this invention is to repeatedly circulate organic wastewater containing sufficient dissolved oxygen through a fixed filter bed filled with a filter medium that has a large specific surface area on which aerobic microorganisms can attach. As a sewage treatment equipment that biochemically oxidizes and decomposes the sewage using epiphytic aerobic microorganisms while filtering and purifying the sewage, the sewage comes into contact with the filter material and is sufficiently decomposed by the microorganisms that have grown on the filter material. It is an object of the present invention to provide a sewage treatment device in which nitrogen bone removal is performed to a high degree, floating matter is almost prevented from flowing into treated water, and surplus sludge is hardly generated.

本考案の上記目的は、好気性微生物の着生し得る比表面
積が大なる濾材が充填固定された濾床に、充分な溶存酸
素を含ませた有機性汚水を反復して循環させながら、濾
材に着生する好気性術生物により生物化学的に酸化分解
しつつ濾過し浄化処理する方式の汚水処理装置に於て、
前記濾床が上段濾床と下段濾床とからなり、該上段濾床
は、汚水が乱流となって流下できるように、汚水を鉛直
方向に対し斜めに誘導できる面を多数備えた複数の濾材
が間隔をおいて並行に配列されてなり、該下段濾床は、
複数の波型板状濾材が上から下へ間隔をおいて水平状に
並行に配列されると共に各隣り合う上下濾材間において
汚水が上側濾材の片端から下側波材上に落下できるよう
に濾材端位置が水平方向にずらされて配列されてなるこ
とを特徴とする有機性汚水処理装置により達成される。
The above object of the present invention is to repeatedly circulate organic wastewater containing sufficient dissolved oxygen through a fixed filter bed filled with a filter medium having a large specific surface area on which aerobic microorganisms can attach. In sewage treatment equipment that biochemically oxidizes and decomposes wastewater using aerobic organisms that grow on it, it filters and purifies it.
The filter bed consists of an upper filter bed and a lower filter bed, and the upper filter bed has a plurality of surfaces that can guide wastewater diagonally with respect to the vertical direction so that the wastewater can flow down in a turbulent flow. The lower filter bed is composed of filter media arranged in parallel at intervals,
A plurality of corrugated plate-shaped filter media are arranged horizontally in parallel at intervals from top to bottom, and the filter media are arranged in such a way that wastewater can fall from one end of the upper filter media onto the lower corrugated media between the adjacent upper and lower filter media. This is achieved by an organic sewage treatment device characterized in that the end positions are shifted in the horizontal direction.

前記上段濾床における濾材は汚水中の窒素成分を好気性
処理して硝酸性窒素或いは亜硝酸性窒素に変換するもの
であり、乱流の効果を強めると共に水量水圧の変動にも
耐えるものとする。
The filter material in the upper filter bed aerobically treats nitrogen components in wastewater and converts them into nitrate nitrogen or nitrite nitrogen, which strengthens the effect of turbulence and also withstands fluctuations in water volume and water pressure. .

この濾材として鉛直方向に対し鋭角に傾斜したネット板
状の濾材、表裏面が波状面である板状濾材にして汚水を
鉛直方向に対し斜めに誘導する面を提供するように波状
面の各山部及び谷部が鉛直方向に対し傾斜したもの等を
挙げられる。
This filter material is a net plate-like filter material that is inclined at an acute angle with respect to the vertical direction, and a plate-like filter material that has wavy surfaces on the front and back surfaces. Examples include those whose portions and valleys are inclined with respect to the vertical direction.

また前記下段濾床としては、波型板状濾材を数枚上から
下へ略水平並行に配列したものを1組とし、これを縦横
夫々数列に並設して構成することができ、高さが充分に
あるときは数段積みにするとよい。
The lower filter bed can be constructed by arranging several corrugated plate-shaped filter media in substantially horizontal parallel from top to bottom, and arranging them in several rows in both length and width. If you have enough, it is a good idea to stack them in several layers.

各濾材の材質としてはプラスチック製のものが好ましい
が、その他の材質のものでも良く、濾材の大きさ、相互
間隔、ネット板状濾材を使用する場合にはそのネットロ
サイズ等は処理汚水の性状、処理規模、処理目的等によ
り適宜に決定される。
The material of each filter medium is preferably plastic, but other materials may also be used.The size of the filter medium, the mutual spacing, and when using a net plate filter medium, the net size, etc. will depend on the properties of the treated sewage. , is determined as appropriate depending on the processing scale, processing purpose, etc.

本考案の処理装置においては、上段濾床上方から供給さ
れて該濾床を流下する汚水は乱流となりなから該濾床濾
材に着生した好気性微生物群と十分反復接触して酸化さ
れ、下段濾床では汚水の流れの殆どの部分が実質上水平
流となり、従って濾材に着生した生物膜乃至汚泥つまり
微生物は剥離されがたく、加えて第5図に示す如く波型
状濾材の上面に好気性微生物層aと嫌気性微生物層すが
重なり、下面に好気性微生物層aが形成されて汚水中の
ピンフロック等浮遊物質の捕捉性が良くなり、処理水中
への浮遊物流出が殆どなくなる。
In the treatment device of the present invention, the wastewater supplied from above the upper filter bed and flowing down the filter bed does not become a turbulent flow, and is oxidized by sufficiently repeatedly contacting the aerobic microorganisms that have grown on the filter media of the filter bed. In the lower filter bed, most of the flow of sewage becomes a substantially horizontal flow, so that biofilm or sludge, or microorganisms, that have grown on the filter medium are difficult to peel off. The aerobic microbial layer a and the anaerobic microbial layer overlap, and the aerobic microbial layer a is formed on the lower surface, which improves the ability to capture suspended solids such as pin flocs in the wastewater, and almost no suspended solids flow into the treated water. It disappears.

そして汚水中の硝酸性窒素は、汚水が下段濾床の波型板
状濾材の上面谷部に着生する嫌気性微生物の雰囲気が強
い下方部分に進むにつれて窒素ガスに変換され、汚水中
の窒素分は十分に除去される。
Nitrate nitrogen in the wastewater is converted to nitrogen gas as the wastewater advances to the lower part where the atmosphere of anaerobic microorganisms that grow in the upper valleys of the corrugated plate filter media in the lower filter bed is strong. minutes are fully removed.

また、本考案の処理装置に於いては、好気的及び嫌気的
微生物の共存併用により、全体として余剰汚泥の発生が
極めて少なくなり汚水は高度に浄化される。
Furthermore, in the treatment apparatus of the present invention, by coexisting aerobic and anaerobic microorganisms, the generation of surplus sludge as a whole is extremely reduced, and sewage is purified to a high degree.

本考案処理装置の前に公知の沈澱分離槽または例えば回
転円板法、散水濾床法、長時間ばつき法等の公知の生物
処理槽等を設けることも可能である。
It is also possible to provide a known sedimentation separation tank or a known biological treatment tank, such as a rotating disk method, a trickling filter method, or a long-time perturbation method, in front of the treatment device of the present invention.

また本考案処理装置の後に沈澱槽を設けても良い。Further, a settling tank may be provided after the treatment apparatus of the present invention.

本考案の汚水処理装置では未処理の生活水をはじめとし
、予め前処理を施した各種の汚水を処理することができ
る。
The sewage treatment apparatus of the present invention can treat various types of sewage that have been pretreated, including untreated domestic water.

かくの如く本考案の汚水処理装置によれば、有機性汚水
を濾材に十分接触させて濾材着生微生物により十分分解
でき、有機性汚水に含まれる窒素成分を容易に窒素ガス
にまで変換して脱窒し、汚水中の窒素成分を高度に除去
でき、BODやCODも大幅に低下して処理水中の有機
物濃度は非常に低くなり且つ安定し、また、下段濾床の
ピンフロック等の捕捉、吸着性が優れることに基づく浮
遊物質の除去率も高く処理水中への浮遊物質の流出が殆
ど防止され、更には下段濾床における好気性及び嫌気性
微生物の共存併用により全体としての余剰汚泥の発生が
極めて少なく、高度の浄化が達成されると共に装置の維
持管理も容易となる。
As described above, according to the sewage treatment apparatus of the present invention, organic sewage can be brought into sufficient contact with the filter medium and sufficiently decomposed by the microorganisms living on the filter medium, and the nitrogen components contained in the organic sewage can be easily converted to nitrogen gas. It can denitrify and highly remove nitrogen components from wastewater, significantly reduce BOD and COD, and the concentration of organic matter in treated water becomes extremely low and stable.It also traps pin flocs in the lower filter bed. The removal rate of suspended solids is high due to its excellent adsorption properties, and the outflow of suspended solids into the treated water is almost prevented, and furthermore, the coexistence of aerobic and anaerobic microorganisms in the lower filter bed reduces the generation of excess sludge as a whole. With this method, a high degree of purification is achieved, and the maintenance of the equipment is also easy.

以下に本考案の実施例を図面にもとづき説明する。Embodiments of the present invention will be described below based on the drawings.

第1図は1実施例の概略断面図であり、この処理装置に
おいては、処理槽1内の中間部分に濾床が配設されてお
り、この濾床は上段濾床6と下段濾床8とから戒ってい
る。
FIG. 1 is a schematic cross-sectional view of one embodiment. In this processing apparatus, a filter bed is disposed in the middle part of the processing tank 1, and this filter bed includes an upper filter bed 6 and a lower filter bed 8. I am admonishing you.

処理槽1上方には空気導管3が架設されていて、この管
から分枝された枝管4が濾床6及び8を貫通して処理槽
1底にまで達している。
An air conduit 3 is installed above the processing tank 1, and a branch pipe 4 branched from this pipe passes through the filter beds 6 and 8 and reaches the bottom of the processing tank 1.

各枝管4にはもう1つの管が外嵌されていてエヤーリフ
トポンプ5が形成されている。
Each branch pipe 4 has another pipe fitted over it to form an air lift pump 5.

上段濾床6は、第2図に示すように、複数のネット板状
濾材を鉛直方向に対し若干傾斜させた状態で間隔をおい
て並行に配列してなるユニット7を複数個上下2段に積
み重ねてなっている。
As shown in FIG. 2, the upper filter bed 6 has a plurality of units 7 arranged in parallel at intervals with a plurality of net plate-shaped filter media slightly inclined with respect to the vertical direction, arranged in two upper and lower stages. They are piled up.

また下段濾床8は複数のユニットからなり、各ユニット
は第4図に示すように、波型板状濾材9を上から下へ間
隔をおいて水平並行に配列すると共に各隣り合う上下濾
材間において汚水が上側濾材の片端から下側濾材上に落
下できるように濾材端位置を水平方向にずらして配列し
てなっている。
The lower filter bed 8 is composed of a plurality of units, and each unit has corrugated plate-shaped filter media 9 arranged horizontally in parallel from top to bottom at intervals, and between adjacent upper and lower filter media. The end positions of the filter media are shifted in the horizontal direction so that wastewater can fall from one end of the upper filter media onto the lower filter media.

2及び10はそれぞれ移流管である。2 and 10 are advection tubes, respectively.

移流管2から処理槽1へ供給された汚水はまず上段濾床
6を流下したのち、下段濾床8を水平流となってジグザ
グに流下し処理槽底に達し、エヤーリフトポンプ5にて
再び溶存酸素を充分含んだ状態で上段濾床上方へ供給さ
れ、斯くして汚水は処理槽内で循環し、濾床6及び8の
微生物群により生物化学的に酸化分解され、脱窒され、
循環処理された水は移流管10から流出する。
The wastewater supplied from the advection pipe 2 to the treatment tank 1 first flows down the upper filter bed 6, then flows down the lower filter bed 8 in a horizontal flow in a zigzag pattern, reaching the bottom of the treatment tank, where it is pumped again by the air lift pump 5. The sewage is supplied above the upper filter bed in a state containing sufficient dissolved oxygen, and is thus circulated within the treatment tank where it is biochemically oxidized and decomposed and denitrified by the microorganisms in the filter beds 6 and 8.
The circulated water flows out from the advection pipe 10.

上段濾床6内を汚水が流下するに除土ては、汚水は鉛直
方向に自重で落下しようとする一方、いたる所にある傾
斜面により鉛直方向に対し斜めにも誘導され、汚水同志
が混ざり合い衝突し合って全体として乱流となる。
When sewage flows down inside the upper filter bed 6, it tries to fall vertically under its own weight, but it is also guided diagonally to the vertical direction by the slopes that are everywhere, and the sewage mixes with other sewage. They collide and collide, creating a turbulent flow as a whole.

上段濾床6を構成する濾材は、上記ネット板状濾材のほ
か、例えば第3図に示す如く、表裏面が波型面である板
状濾材にして汚水を鉛直方向に対し斜めに誘導できる面
を提供するように、波型面の各山部及び谷部が鉛直方向
に対し傾斜した濾材であってもよい。
In addition to the above-mentioned net plate-shaped filter media, the filter media constituting the upper filter bed 6 may be a plate-shaped filter media whose front and back surfaces are corrugated, as shown in FIG. The filter medium may have peaks and troughs of the corrugated surface inclined with respect to the vertical direction so as to provide the following.

第1図に示す実施例では処理槽は1つだけであるが斯か
る処理槽を複数個連設して用いることもできる。
In the embodiment shown in FIG. 1, there is only one processing tank, but a plurality of such processing tanks can be used in series.

上段濾床の濾材の大きさ、個数、その傾斜の方向、手段
濾床の濾材の大きさ、個数、1つの濾材端から次段濾材
上に臨む開口の面積等は、上記実施例に示されるほか、
被処理汚水の性状、処理目的、処理量等に応じて適宜決
定されうる。
The size, number and direction of inclination of the filter media in the upper stage filter bed, the size and number of filter media in the means filter bed, the area of the opening facing the next stage filter media from the end of one filter media, etc. are shown in the above examples. others,
It can be determined as appropriate depending on the properties of the wastewater to be treated, the purpose of treatment, the amount of treatment, etc.

以下に本発明装置の浄化性能を、実施例により示すと次
の通りである。
The purification performance of the device of the present invention will be shown below using Examples.

上記実施例から明らかなように本考案の処理装置により
極めて高度の汚水浄化が達成されることが明らかで゛あ
る。
As is clear from the above examples, it is clear that extremely high level of sewage purification can be achieved by the treatment apparatus of the present invention.

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

第1図は本考案の1実施例の概略縦断面図、第2図及び
第3図はそれぞれ本考案処理装置における上段濾床に適
用されるネット板状濾材及び波状の板状濾材の斜面図、
第4図は本考案処理装置における下段濾床に適用される
濾材の1例を示す斜面図、第5図は下段濾床の波型林状
濾材に形成される微生物層を示す説明図である。 尚図において 1は処理槽、2は移流管、3は空気導管
、4は空気枝管、5はエアーリフトポンプ管、6は上段
濾床、7は濾材、8は下段濾床、9は濾材、10は移流
管である。
FIG. 1 is a schematic vertical sectional view of one embodiment of the present invention, and FIGS. 2 and 3 are slope views of a net plate filter medium and a wavy plate filter medium applied to the upper filter bed in the processing apparatus of the present invention, respectively. ,
FIG. 4 is a perspective view showing an example of a filter medium applied to the lower filter bed in the processing apparatus of the present invention, and FIG. 5 is an explanatory diagram showing a microbial layer formed on the wave-shaped forest filter medium of the lower filter bed. . In the figure, 1 is a treatment tank, 2 is an advection pipe, 3 is an air conduit, 4 is an air branch pipe, 5 is an air lift pump pipe, 6 is an upper filter bed, 7 is a filter medium, 8 is a lower filter bed, and 9 is a filter medium , 10 is an advection tube.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 好気性微生物の着生し得る比表面積が大なる濾材が充填
固定された濾床に、充分な溶存酸素を含ませた有機性汚
水を反復して循環させながら、濾材に着生する好気性微
生物により生物化学的に酸化分解しつつ濾過し浄化処理
する方式の汚水処理装置に於て、前記濾床が上段濾床と
下段濾床とからなり、該上段濾床は、汚水が乱流となっ
て流下できるように、汚水を鉛直方向に対し斜めに誘導
できる面を多数備えた複数の濾材が間隔をおいて並行に
配列されてなり、該下段濾床は、複数の波型板状濾材が
上から下へ間隔をおいて水平状に並行に配列されると共
に各隣り合う上下濾材間において汚水が上側濾材の片端
から下側濾材上に落下できるように濾材端位置が水平方
向にずらされて配列されてなることを特徴とする有機性
汚水処理装置。
Aerobic microorganisms grow on the filter bed by repeatedly circulating organic sewage containing sufficient dissolved oxygen through a fixed filter bed filled with filter media that has a large specific surface area on which aerobic microorganisms can grow. In a sewage treatment device that performs filtration and purification treatment while being biochemically oxidized and decomposed by A plurality of filter media each having a large number of surfaces capable of guiding wastewater diagonally to the vertical direction are arranged in parallel at intervals so that the wastewater can flow down. The filter media are arranged horizontally in parallel at intervals from top to bottom, and the end positions of the filter media are shifted in the horizontal direction between each adjacent upper and lower filter media so that wastewater can fall from one end of the upper filter media onto the lower filter media. An organic sewage treatment device characterized by being arranged in an array.
JP1980102581U 1980-07-18 1980-07-18 organic sewage treatment equipment Expired JPS5855996Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1980102581U JPS5855996Y2 (en) 1980-07-18 1980-07-18 organic sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1980102581U JPS5855996Y2 (en) 1980-07-18 1980-07-18 organic sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPS5725795U JPS5725795U (en) 1982-02-10
JPS5855996Y2 true JPS5855996Y2 (en) 1983-12-22

Family

ID=29464002

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1980102581U Expired JPS5855996Y2 (en) 1980-07-18 1980-07-18 organic sewage treatment equipment

Country Status (1)

Country Link
JP (1) JPS5855996Y2 (en)

Also Published As

Publication number Publication date
JPS5725795U (en) 1982-02-10

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