JPH039836Y2 - - Google Patents

Info

Publication number
JPH039836Y2
JPH039836Y2 JP5350285U JP5350285U JPH039836Y2 JP H039836 Y2 JPH039836 Y2 JP H039836Y2 JP 5350285 U JP5350285 U JP 5350285U JP 5350285 U JP5350285 U JP 5350285U JP H039836 Y2 JPH039836 Y2 JP H039836Y2
Authority
JP
Japan
Prior art keywords
separator
liquid
waste liquid
tank
suspended solids
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
JP5350285U
Other languages
Japanese (ja)
Other versions
JPS61171600U (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 JP5350285U priority Critical patent/JPH039836Y2/ja
Publication of JPS61171600U publication Critical patent/JPS61171600U/ja
Application granted granted Critical
Publication of JPH039836Y2 publication Critical patent/JPH039836Y2/ja
Expired legal-status Critical Current

Links

Classifications

    • Y02W10/12

Landscapes

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

Description

【考案の詳細な説明】 〈産業上の利用分野〉 本考案は産業排水、下水、し尿等の有機性廃液
を上向流スラツジブランケツト法を用いて嫌気性
処理を行う際の廃液処理槽の改良に関するもので
ある。
[Detailed description of the invention] <Industrial application field> This invention is a waste liquid treatment tank for anaerobically treating organic waste liquids such as industrial wastewater, sewage, human waste, etc. using the upward flow sludge blanket method. This is related to the improvement of

〈従来の技術〉 比較的高濃度のBOD成分を含む廃液を嫌気性
微生物を用いて処理する場合、その一種として従
来から第2図に示したようなスラツジブランケツ
ト法による廃液処理槽が用いられている。
<Prior art> When waste liquid containing a relatively high concentration of BOD components is treated using anaerobic microorganisms, a waste liquid treatment tank using the sludge blanket method as shown in Fig. 2 has traditionally been used. It is being

すなわち槽1の下方部に嫌気性微生物のブラン
ケツトゾーン2を有し、当該ブランケツトゾーン
2の上方部に、遮蔽板3と当該遮蔽板3の上部に
位置する円錐形あるいは角錐形の補集板4からな
る末広がりの補集室Sを有するセパレータ5を設
置し、当該セパレータ5に発生ガス取り出し管6
を連通するとともに槽1の上部に処理液流出管7
を連通したもので、有機性廃液を槽1の底部に連
通した廃液流入管8から流入して、廃液を前記ブ
ランケツトゾーン2に接触させてここで嫌気性処
理により廃液中のBOD成分を除去するものであ
る。なお嫌気性処理によりメタンガス、炭酸ガス
等のガスが発生するが、当該発生ガスは気泡状と
なつて処理液とともにブランケツトゾーン2を離
脱し、図中点線の矢印線で示したごとく末広がり
の補集室Sを有するセパレータ5により補集し、
発生ガス取り出し管6より槽1外部へ取り出し、
一方処理液は実線の矢印線で示したごとくセパレ
ータ5を通過させて槽1上部の処理液流出管7よ
り流出させるものである。
That is, there is a blanket zone 2 for anaerobic microorganisms in the lower part of the tank 1, and in the upper part of the blanket zone 2, there is a shielding plate 3 and a conical or pyramid-shaped collection located above the shielding plate 3. A separator 5 having a collection chamber S that widens toward the end and is made of a plate 4 is installed, and a generated gas extraction pipe 6 is installed in the separator 5.
At the same time, a processing liquid outflow pipe 7 is connected to the upper part of the tank 1.
The organic waste liquid flows in from the waste liquid inflow pipe 8 that communicates with the bottom of the tank 1, and the waste liquid is brought into contact with the blanket zone 2, where BOD components in the waste liquid are removed by anaerobic treatment. It is something to do. Note that gases such as methane gas and carbon dioxide gas are generated by the anaerobic treatment, but the generated gases become bubbles and leave the blanket zone 2 together with the treatment liquid, resulting in compensation for the end expansion as shown by the dotted arrow line in the figure. Collected by a separator 5 having a collection chamber S,
The generated gas is taken out from the tank 1 through the take-out pipe 6,
On the other hand, the processing liquid is allowed to pass through the separator 5 and flow out from the processing liquid outflow pipe 7 at the upper part of the tank 1, as shown by the solid arrow line.

なお処理液中には多少の懸濁固形物を有する
が、当該懸濁固形物の一部はセパレータ5の補集
室S内で沈降させ、また他部はセパレータ5の上
方で沈降させ、補集板4の斜面を介して下方に落
下させるものである。またセパレータ5の補集室
S内の発生ガスの圧力を調整して、補集室内に液
面Lを形成し、発生ガス取り出し管6から発生ガ
スのみを取り出すようにしている。
Note that the treatment liquid contains some suspended solids, and some of the suspended solids are allowed to settle in the collection chamber S of the separator 5, and the other part is allowed to settle above the separator 5. It is made to fall downward through the slope of the collecting board 4. Further, the pressure of the generated gas in the collection chamber S of the separator 5 is adjusted to form a liquid level L in the collection chamber, and only the generated gas is taken out from the generated gas extraction pipe 6.

〈解決しようとする問題点〉 前述したスラツジブランケツト法による廃液処
理槽は、標準的な嫌気性活性汚泥法と比較して高
負荷処理が可能で、また嫌気性固定床に比較して
充填材が不要であるため建設費が比較的安価であ
るという利点を有するが、以下のような欠点があ
る。
<Problem to be solved> The waste liquid treatment tank using the sludge blanket method described above is capable of high-load treatment compared to the standard anaerobic activated sludge method, and is also easier to fill than an anaerobic fixed bed. Although it has the advantage of being relatively inexpensive to construct because no materials are required, it has the following drawbacks.

すなわち嫌気処理により発生したガスが気泡状
となつてブランケツトゾーン2を離脱する際、当
該気泡が懸濁固形物を抱き込み、当該懸濁固形物
が補集室S内の水面Lに浮上し、しだいに層状を
呈して水面Lに蓄積するという問題を起こす。
That is, when the gas generated by the anaerobic treatment becomes bubbles and leaves the blanket zone 2, the bubbles enclose suspended solids, and the suspended solids float to the water surface L in the collection chamber S. , which causes the problem that it gradually forms a layer and accumulates on the water surface L.

このような状態となるとセパレータ5による発
生ガスの補集に障害を受け、懸濁固形物を抱き込
んだ気泡の一部がセパレータ5を通過して槽1の
上方に混入し、処理液の懸濁固形物量が増加する
などの種々の障害を起こす。
In such a state, the collection of generated gas by the separator 5 is impaired, and some of the bubbles enclosing the suspended solids pass through the separator 5 and enter the upper part of the tank 1, causing suspension of the processing liquid. This causes various problems such as an increase in the amount of turbid solids.

本考案は従来の廃液処理槽におけるかかる欠点
を解決し、補集室S内の水面Lに懸濁固形物を浮
上させないことを目的とするものである。
The purpose of the present invention is to solve such drawbacks in conventional waste liquid treatment tanks and to prevent suspended solids from floating on the water surface L in the collection chamber S.

〈問題点を解決する手段〉 本考案は嫌気性微生物のブランケツトゾーンを
有する槽の下部から有機物を含む廃液を流入して
廃液と前記ブランケツトゾーンとを接触させて嫌
気処理を行い、前記ブランケツトゾーンを通過し
た発生ガス気泡と処理液と懸濁固形物の気液固の
三相混合物を末広がりの補集室からなるセパレー
タに通過させ、発生ガスを当該セパレータで補集
し、処理液を槽の上方部で取り出す廃液処理槽に
おいて、前記ブランケツトゾーンと当該セパレー
タの間の気液固の三相混合ゾーンに傾斜板あるい
は傾斜管を設置したことを特徴とする廃液処理槽
に関するものである。
<Means for Solving the Problems> The present invention introduces waste liquid containing organic matter from the bottom of a tank having a blanket zone for anaerobic microorganisms, brings the waste liquid into contact with the blanket zone, performs anaerobic treatment, and The three-phase gas-liquid-solid mixture of generated gas bubbles, treated liquid, and suspended solids that has passed through the ket zone is passed through a separator consisting of a collecting chamber that widens at the end, the generated gas is collected by the separator, and the treated liquid is The present invention relates to a waste liquid treatment tank in which waste liquid is taken out at the upper part of the tank, characterized in that an inclined plate or an inclined pipe is installed in a gas-liquid-solid three-phase mixing zone between the blanket zone and the separator. .

第1図は本考案の実施態様の一例を示す説明図
であり、本考案は従来の廃液処理槽におけるブラ
ンケツトゾーン2とセパレータ5の間の気液固の
三相混合ゾーンに傾斜板9を設置したものであ
る。なお他の部分は従来のものと同様なので説明
を省略する。
FIG. 1 is an explanatory diagram showing an example of an embodiment of the present invention, and the present invention includes an inclined plate 9 in a three-phase gas-liquid-solid mixing zone between a blanket zone 2 and a separator 5 in a conventional waste liquid treatment tank. It was installed. Note that the other parts are the same as those of the conventional one, so the explanation will be omitted.

〈作用〉 本考案において有機性廃液を処理する場合は、
廃液流入管8から有機性廃液を流入し、廃液を嫌
気性微生物のブランケツトゾーン2に接触させ
る。当該ブランケツトゾーン内の嫌気性微生物の
働きにより廃液中のBOD成分は分解され、同時
にメタンガスあるいは炭酸ガス等のガスが発生す
る。当該発生ガスは気泡状となつて処理液および
懸濁固形物と共に、さらに気泡に懸濁固形物の一
部を抱き込んでブランケツトゾーン2を離脱する
が、ブランケツトゾーン2の上部に設置された傾
斜板9を通過する際に、傾斜板9と水流の衝突に
より懸濁固形物を抱き込んだ気泡が破壊され、懸
濁固形物は図中の一点鎖線の矢印線で示したごと
く下方に沈降し、またこのように懸濁固形物を除
去された気泡が点線の矢印線で示したごとく上昇
しセパレータ5によつて補集される。さらに気泡
および大部分の懸濁物が除かれた処理液は実線の
矢印線で示したごとくセパレータ5を通過し、処
理液流出管7より流出する。
<Function> When treating organic waste liquid in this invention,
Organic waste liquid flows in from the waste liquid inflow pipe 8 and is brought into contact with the blanket zone 2 of anaerobic microorganisms. The BOD components in the waste liquid are decomposed by the action of anaerobic microorganisms in the blanket zone, and at the same time gases such as methane gas or carbon dioxide gas are generated. The generated gas forms bubbles and leaves the blanket zone 2, entrapping some of the suspended solids in the bubbles together with the processing liquid and suspended solids. When passing through the tilted plate 9, the air bubbles enclosing the suspended solids are destroyed by the collision between the tilted plate 9 and the water flow, and the suspended solids move downward as shown by the dash-dotted arrow line in the figure. The air bubbles that settle and have the suspended solids removed in this manner rise as indicated by the dotted arrow line and are collected by the separator 5. Further, the processing liquid from which air bubbles and most of the suspended matter have been removed passes through the separator 5 as shown by the solid arrow line, and flows out from the processing liquid outflow pipe 7.

本考案に用いる傾斜板9としては、一般の凝集
沈澱装置の固液分離を促進させる用途に用いる傾
斜板と同様なものを用いることができ、傾斜板9
の設置高さは0.5〜1mぐらいで充分である。な
お傾斜板9に代えて同様な作用を有する傾斜管も
用いることができる。
The inclined plate 9 used in the present invention can be similar to the inclined plate used for promoting solid-liquid separation in a general coagulation-sedimentation apparatus, and the inclined plate 9
An installation height of about 0.5 to 1 m is sufficient. Incidentally, instead of the inclined plate 9, an inclined pipe having a similar function can also be used.

〈効果〉 以上説明したごとく本考案はブランケツトゾー
ン2とセパレータ5の間の気液固の三相混合ゾー
ンに設置した傾斜板あるいは傾斜管の働きによ
り、懸濁固形物を抱き込んだ気泡を破壊するの
で、補集室S内の水面Lに懸濁固形物が浮上する
ことなく、したがつてセパレータ5における発生
ガスの補集が効果的に行われる。
<Effects> As explained above, the present invention uses the function of the inclined plate or inclined pipe installed in the three-phase gas-liquid-solid mixing zone between the blanket zone 2 and the separator 5 to eliminate air bubbles that enclose suspended solids. Since the separator 5 is destroyed, the suspended solids do not float to the water surface L in the collection chamber S, and the generated gas is effectively collected in the separator 5.

また本考案の傾斜板あるいは傾斜管の作用は上
述したごとく懸濁固形物を抱き込んだ気泡の破壊
とともに、懸濁固形物そのものの沈降促進にも効
果がある。
Furthermore, the action of the inclined plate or inclined tube of the present invention is effective in destroying the bubbles entrapping the suspended solids as described above, as well as promoting the settling of the suspended solids themselves.

以上のような効果により、ブランケツトゾーン
2内の微生物が増加し、水質変動、水量変動に対
する安定性が増加するとともに、処理液の懸濁固
形物量を低下させることができる。
As a result of the above effects, the number of microorganisms in the blanket zone 2 increases, stability against changes in water quality and water amount increases, and the amount of suspended solids in the treatment liquid can be reduced.

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

第1図は本考案の実施態様の一例を示す説明図
であり、第2図は従来の廃液処理槽の説明図であ
る。 1……槽、2……ブランケツトゾーン、3……
遮蔽板、4……補集板、5……セパレータ、6…
…発生ガス取り出し管、7……処理液流出管、8
……廃液流入管、9……傾斜板、S……補集室、
L……水面。
FIG. 1 is an explanatory diagram showing an example of an embodiment of the present invention, and FIG. 2 is an explanatory diagram of a conventional waste liquid treatment tank. 1...tank, 2...blanket zone, 3...
Shielding plate, 4... Collection plate, 5... Separator, 6...
... Generated gas take-off pipe, 7... Processing liquid outflow pipe, 8
...Waste liquid inflow pipe, 9...Slanted plate, S...Collection chamber,
L...Water surface.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 嫌気性微生物のブランケツトゾーンを有する槽
の下部から有機物を含む廃液を流入して廃液と前
記ブランケツトゾーンとを接触させて嫌気処理を
行い、前記ブランケツトゾーンを通過した発生ガ
ス気泡と処理液と懸濁固形物の気液固の三相混合
物を末広がりの補集室からなるセパレータに通過
させ、発生ガスを当該セパレータで補集し、処理
液を槽の上方部で取り出す廃液処理槽において、
前記ブランケツトゾーンと当該セパレータの間の
気液固の三相混合ゾーンに傾斜板あるいは傾斜管
を設置したことを特徴とする廃液処理槽。
A waste liquid containing organic matter is introduced from the lower part of a tank having a blanket zone for anaerobic microorganisms, and the waste liquid is brought into contact with the blanket zone to perform anaerobic treatment, and the generated gas bubbles that have passed through the blanket zone and the treated liquid are In a waste liquid treatment tank, a three-phase gas-liquid-solid mixture of suspended solids and suspended solids is passed through a separator consisting of a collecting chamber that widens toward the end, the generated gas is collected by the separator, and the treated liquid is taken out at the upper part of the tank.
A waste liquid treatment tank characterized in that an inclined plate or an inclined pipe is installed in a gas-liquid-solid three-phase mixing zone between the blanket zone and the separator.
JP5350285U 1985-04-12 1985-04-12 Expired JPH039836Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5350285U JPH039836Y2 (en) 1985-04-12 1985-04-12

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5350285U JPH039836Y2 (en) 1985-04-12 1985-04-12

Publications (2)

Publication Number Publication Date
JPS61171600U JPS61171600U (en) 1986-10-24
JPH039836Y2 true JPH039836Y2 (en) 1991-03-12

Family

ID=30574426

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5350285U Expired JPH039836Y2 (en) 1985-04-12 1985-04-12

Country Status (1)

Country Link
JP (1) JPH039836Y2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5600525B2 (en) * 2010-08-31 2014-10-01 株式会社神鋼環境ソリューション Upflow type reaction tank, water treatment method using the reaction tank, and water treatment apparatus provided with the reaction tank

Also Published As

Publication number Publication date
JPS61171600U (en) 1986-10-24

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