JPH0642793Y2 - Aerobic immersion ▲ Floor ▼ Floor equipment - Google Patents

Aerobic immersion ▲ Floor ▼ Floor equipment

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Publication number
JPH0642793Y2
JPH0642793Y2 JP1990023664U JP2366490U JPH0642793Y2 JP H0642793 Y2 JPH0642793 Y2 JP H0642793Y2 JP 1990023664 U JP1990023664 U JP 1990023664U JP 2366490 U JP2366490 U JP 2366490U JP H0642793 Y2 JPH0642793 Y2 JP H0642793Y2
Authority
JP
Japan
Prior art keywords
immersion
water
bed
floor
cleaning
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 - Fee Related
Application number
JP1990023664U
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Japanese (ja)
Other versions
JPH03115099U (en
Inventor
克之 片岡
Original Assignee
荏原インフイルコ株式会社
株式会社荏原総合研究所
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Priority to JP1990023664U priority Critical patent/JPH0642793Y2/en
Publication of JPH03115099U publication Critical patent/JPH03115099U/ja
Application granted granted Critical
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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

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  • Biological Treatment Of Waste Water (AREA)

Description

【考案の詳細な説明】 〔産業上の利用分野〕 本考案は、下水,し尿系汚水,各種有機性産業廃水など
のBOD,SS等を含む有機性汚水を極めて効果的に浄化処理
する生物処理装置に関するものである。
[Detailed Description of the Invention] [Industrial field of application] The present invention is a biological treatment for extremely effectively purifying organic sewage containing BOD, SS, etc. such as sewage, night soil sewage, and various organic industrial wastewater. It relates to the device.

〔従来の技術〕[Conventional technology]

従来より、第2図に示す好気性浸漬床装置が広く公知
である(公害と対策誌Vo1.20,No.13,pp41〜46(84)参
照)。この従来の装置は、槽21の水面下に、アンスラサ
イト,粒状活性炭,各種粒状鉱物,プラスチック粒子,
粒状スポンジなど任意の粒状材の充填層(浸漬床22
と呼ぶ)を設け、該浸漬床22の下部に空気の散気管23
を配設したものである。
2. Description of the Related Art Conventionally, the aerobic submerged bed apparatus shown in FIG. 2 is widely known (see Pollution and Countermeasures Magazine Vo1.20, No. 13, pp 41-46 (84)). This conventional device has an anthracite, granular activated carbon, various granular minerals, plastic particles,
Packed layer of any granular material such as granular sponge (immersion bed 22
Is provided, and an air diffusing pipe 23 is provided below the immersion floor 22.
Is provided.

しかして、有機性汚水(原水)は、沈殿池24から原水流
入管25を経て槽21内に流入し、浸漬床22を下向流また
は上向流(第2図は下向流の場合)で流過し、粒状材
表面の微生物および空気ブロワー26から散気管23を経て
散気される空気泡と接触し、BODが除去されると共に、
原水SSも過除去され、処理水となって処理流出管27を
経て処理水槽28に至る。このような処理を継続するにつ
れ、浸漬床22内に捕捉されたSSと微生物量の増加によ
って、過抵抗が増加し処理を続けることが困難になる
ので、処理水槽28内に貯留されている清澄な処理水を洗
浄ポンプ29によって浸漬床22の下部に供給し、浸漬
床22を洗浄する。
Then, the organic sewage (raw water) flows into the tank 21 from the settling tank 24 through the raw water inflow pipe 25 and flows downward or upward in the immersion bed 22 (in the case of downward flow in FIG. 2). At the same time, the microbes on the surface of the granular material and the air blower 26 come into contact with the air bubbles diffused through the air diffuser 23, and BOD is removed,
The raw water SS is also excessively removed and becomes treated water, and reaches the treated water tank 28 through the treated outflow pipe 27. As such a treatment is continued, the SS trapped in the immersion bed 22 and the increase in the amount of microorganisms increase the over resistance and make it difficult to continue the treatment. The treated water is supplied to the lower part of the immersion floor 22 by the cleaning pump 29 to clean the immersion floor 22.

浸漬床22の洗浄排水は、洗浄排水槽30を経て沈殿池24
に供給されてSSが沈降分離され、原水と洗浄排水流量と
の合計量が再び浸漬床22へ供給される。
The cleaning drainage of the immersion floor 22 is passed through the cleaning drainage tank 30 and settling tank 24.
And SS are separated by sedimentation, and the total amount of the raw water and the flow rate of washing waste water is again supplied to the immersion bed 22.

31は洗浄用ブロワーで、逆洗空気管32に連なっている。A blower 31 for cleaning is connected to the backwash air pipe 32.

〔考案が解決しようとする課題〕[Problems to be solved by the device]

しかしながら、第2図の従来装置は、原水SSとBODが低
濃度の場合は極めてすぐれた性能を発揮するが、原水SS
とBODが高濃度の場合は浸漬床22の目づまりの進行度
が大きく、過抵抗の増加が早いので、浸漬床22の洗
浄頻度を頻繁に(例えば1日4〜5回)行わなければな
らない。しかし、浸漬床22の洗浄用水は処理水を使用
しなければならないので(従来知られているすべての浸
漬床装置では、例外なく処理水を用いて浸漬床を洗
浄している)、浸漬床22の洗浄頻度に正比例して処理
水生産量が減少し、例えばQm3/日の原水を浸漬床22
で生物処理しても、たかだか0.5〜0.6Qm3/日程度の処
理水しか得られない。従って、原水BOD,SSが非常に高濃
度の場合は、Qm3/日の原水を通水しても、0.1Qm3/日
以下の処理水しか得られず、残りの処理水0.9Qm3/日以
上は、すべて浸漬床22の洗浄用水として消費されてし
まうことになる。
However, the conventional device shown in Fig. 2 exhibits excellent performance when the raw water SS and BOD are at low concentrations.
If the BOD is high, the degree of clogging of the immersion bed 22 is large and the increase in overresistance is rapid, so the cleaning frequency of the immersion bed 22 must be frequent (for example, 4 to 5 times a day). However, since the water for cleaning the immersion floor 22 must use the treated water (in all the conventionally known immersion bed apparatuses, the treated water is used to wash the immersion floor without exception). The treated water production decreases in direct proportion to the cleaning frequency of, for example, Qm 3 / day of raw water
Even if biological treatment is carried out at, only treated water of about 0.5 to 0.6 Qm 3 / day can be obtained. Therefore, when the raw water BOD and SS are extremely high in concentration, even if the raw water is passed through Qm 3 / day, only treated water of 0.1 Qm 3 / day or less is obtained, and the remaining treated water is 0.9 Qm 3 / day. All the days or more will be consumed as water for cleaning the immersion floor 22.

この結果、従来の浸漬床装置では、例えば原水BOD200
mg/l,SS100mg/l以上の原水には適用できず、適用範囲が
極めて狭かった。この点は従来装置の最大欠点であり、
原水BODが高い場合は、浸漬床装置の前段に、他の生
物処理手段(活性汚泥など)を設けなければならず、ま
た原水SSが高濃度の場合は、第2図のように浸漬床装
置の前段に沈殿池24などを設けなければならず、設置面
積,建設費がかさむものになっていた。
As a result, in conventional immersion bed equipment, for example, raw water BOD200
It could not be applied to raw water above 100 mg / l and SS100 mg / l, and its application range was extremely narrow. This is the biggest drawback of the conventional device,
If the raw water BOD is high, other biological treatment means (such as activated sludge) must be installed in front of the immersion bed device, and if the raw water SS has a high concentration, as shown in Fig. 2, the immersion bed device is used. Settling basin 24 etc. had to be installed in the previous stage, and the installation area and construction cost were high.

また、浸漬床22の目づまり時の洗浄水量(QW)は、
床容積(VM)の2倍、即ち、QW=2VMを必要とするの
で、容積2VM(m3)の処理水貯槽28(洗浄用水貯槽)
と、容積2VM(m3)の洗浄排水槽30を必要とし、これら
の槽の設置面積が浸漬床装置本体よりも大きくなって
しまうという重大な不合理性があった。
Also, the amount of cleaning water (Q W ) when the immersion floor 22 is clogged is
Since it requires twice the floor volume (V M ), that is, Q W = 2 V M , the treated water storage tank 28 (washing water storage tank) has a volume of 2 V M (m 3 ).
Therefore, there was a serious irrationality that the cleaning drainage tank 30 with a volume of 2 V M (m 3 ) was required, and the installation area of these tanks became larger than the immersion floor device main body.

本考案は、前記の従来装置の諸欠点を完全に解決するこ
とを課題とするもので、具体的には、 高濃度の有機性汚水に対しても、極めて容易に浸漬
床装置のみで対応できるようにし、浸漬床の前段に他
の前処理工程(即ち浸漬床への負荷低減工程)を設け
る必要をなくすこと(適用範囲の大幅な拡大化)。
The present invention aims to completely solve the above-mentioned drawbacks of the conventional apparatus. Specifically, even a high concentration of organic sewage can be extremely easily dealt with only by the immersion bed apparatus. In this way, it is possible to eliminate the need for providing another pretreatment step (that is, a step of reducing the load on the immersion bed) in the preceding stage of the immersion bed (a large expansion of the application range).

浸漬床の洗浄に清澄処理水を一切浪費しないですむ
ようにすること(処理水生産効率の大幅な向上)。
Do not waste any clarified treated water for cleaning the submerged floor (significantly improved treated water production efficiency).

大容量の洗浄排水貯槽,洗浄用水貯槽を不要にするこ
と。
Eliminate the need for a large-capacity cleaning drainage storage tank and cleaning water storage tank.

建設費と設置面積を大きく節減すること。Significant savings in construction costs and footprint.

を目的としている。It is an object.

〔課題を解決するための手段〕[Means for Solving the Problems]

本考案は、原水流入部と処理水流出部を設けた槽内に粒
状材を充填した浸漬床を設け、該浸漬床の下部に
酸素含有ガスの散気装置を配備した好気性浸漬床装置
において、前記浸漬床の洗浄排水流出路を固液分離装
置に連通し、該固液分離装置の分離水を前記浸漬床の
下部に圧送する洗浄手段を設けたことを特徴とする好気
性浸漬床装置であり、また前記処理水流出部から流出
する処理水の一部を前記固液分離装置の分離水に補給す
る補給手段を付設したことを特徴とする好気性浸漬床
装置である。
The present invention relates to an aerobic immersion bed apparatus in which an immersion bed filled with a granular material is provided in a tank provided with a raw water inflow section and a treated water outflow section, and an oxygen-containing gas diffuser is provided below the immersion bed. An aerobic submerged bed apparatus comprising: a washing means for communicating the washing drainage outflow passage of the submerged bed with a solid-liquid separator, and pumping the separated water of the solid-liquid separator under the submerged bed. The aerobic submerged bed apparatus is characterized in that a replenishing means for replenishing a part of the treated water flowing out from the treated water outflow portion to the separated water of the solid-liquid separator is attached.

〔作用〕[Action]

上記構成の本考案の作用は、第1図に示すように、原水
である有機性汚水(BOD,SSが高濃度であっても問題な
い)が、槽1内上部に流入し、下向流で浸漬床4内を
流下し、散気装置から吐出される空気泡と生物膜に接触
することによって、溶解性BODが除去され、かつSSも
過除去される。そして、槽1下部からBODとSSなどが高
度に除去された清澄な処理水が処理水流出管3から流出
する。
As shown in FIG. 1, the function of the present invention having the above-described structure is that the raw organic water (there is no problem even if the concentration of BOD and SS is high) flows into the upper part of the tank 1 and flows downward. By flowing down in the immersion bed 4 and contacting the air bubbles discharged from the air diffuser and the biofilm, soluble BOD is removed and SS is also excessively removed. Then, clear treated water from which BOD and SS have been highly removed from the bottom of the tank 1 flows out from the treated water outflow pipe 3.

このような処理を継続すると、ある時点で過抵抗が設
定値に達するので、その時点で浸漬床4の洗浄を行
う。洗浄は次のように行う。即ち、原水を止め、洗浄用
空気を供給し、洗浄用水貯槽11の水を洗浄ポンプ12によ
って浸漬床4の下部に圧送し、浸漬床4の粒状材
を膨張流動化させてSSを洗い出す。多量のSSを含んだ洗
浄排水は槽1の上部から洗浄排水管8を経て流出し、必
要に応じて高分子凝集剤が注入され、固液分離装置9に
おいて生成フロックが急速に分離され、SS10〜15mg/l程
度の清澄な分離水が得られ、洗浄用水として再利用され
る。
If such a process is continued, the over-resistance reaches the set value at a certain point, so that the immersion floor 4 is washed at that point. Washing is performed as follows. That is, the raw water is stopped, the cleaning air is supplied, the water in the cleaning water storage tank 11 is pressure-fed to the lower part of the immersion bed 4 by the cleaning pump 12, and the granular material of the immersion bed 4 is expanded and fluidized to wash out SS. Washing wastewater containing a large amount of SS flows out from the upper part of the tank 1 through the washing drainage pipe 8, a polymer flocculant is injected as needed, and the flocs generated are rapidly separated in the solid-liquid separation device 9, and SS10 About 15 mg / l of clear separated water is obtained and reused as washing water.

このように、浸漬床4の洗浄排水それ自身を、再び浸
漬床4の洗浄用水として供給,再利用するというクロ
ーズトシステム的構成に、本考案の最重要骨子が存す
る。
In this way, the most important essence of the present invention lies in a closed system configuration in which the cleaning wastewater itself of the immersion floor 4 is supplied again as cleaning water for the immersion floor 4 and reused.

なお、固液分離装置9からの排泥量に応じ、処理水貯槽
15から、少量の清澄な処理水を前記洗浄用水に補給でき
るようにしておくことが好ましい。
Depending on the amount of sludge discharged from the solid-liquid separator 9, the treated water storage tank
From 15, it is preferable that a small amount of clear treated water can be supplied to the washing water.

しかして、洗浄排水中のSSが少量になった(浸漬床4
の洗浄が充分行われたことを意味する)時点で、洗浄ポ
ンプ12を止め、再び原水を供給し、生物処理を再開す
る。
Then, the amount of SS in the cleaning drainage became small (immersion floor 4
(Which means that the washing was performed sufficiently), the washing pump 12 is stopped, raw water is supplied again, and the biological treatment is restarted.

なお、浸漬床4の洗浄時に原水供給を止めるのが好ま
しくない場合は、複数の浸漬床4を並設し、洗浄時間
をずらしておけば、常に原水をいずれかの浸漬床に供
給できるので好適である。
If it is not desirable to stop the supply of raw water during the cleaning of the immersion floor 4, it is preferable to arrange a plurality of immersion beds 4 side by side and stagger the cleaning time so that the raw water can always be supplied to one of the immersion beds. Is.

また、本考案では、浸漬床4の前段に、従来のような
沈殿槽や前もってBODを除去するための工程を設ける必
要は格別ないが、このような前処理工程を設けてはなら
ないという意味ではなく、当然設けてもかまわない。特
に、既設の設備を有効利用できるケースでは、前処理工
程を設けて浸漬床4の洗浄頻度を減少させるようにし
て良いことは申すまでもない。
Further, in the present invention, it is not necessary to provide a conventional settling tank or a step for removing BOD in advance in the preceding stage of the immersion bed 4, but in the sense that such a pretreatment step should not be provided. Of course, it does not matter if it is provided. In particular, in the case where existing equipment can be effectively used, it goes without saying that a pretreatment process may be provided to reduce the frequency of cleaning the immersion floor 4.

〔実施例〕〔Example〕

本考案の一実施例を第1図を参照しつつ説明すれば、上
部に原水流入管2、下部に処理水流出管3が開口した槽
1内には、アンスラサイト,各種粒状鉱物,粒状活性
炭,プラスチック粒子その他の任意の粒状材を充填し
た浸漬床4が設けられており、比重が1.0以上の沈降
性粒状材を使用するときは、浸漬床4の下部を支持
部材5で支持し、比重1.0未満の浮上性粒状材を使用
するきは、浸漬床4の上部に浮上性粒状材の流出を
阻止するネットなどの多孔通水部材5′を設ける。この
支持部材5又は浮上性浸漬床の下部にはエアレーショ
ン用の散気管6が配備され、空気ブロワー7に連なって
いる。
An embodiment of the present invention will be described with reference to FIG. 1. An anthracite, various kinds of granular minerals and granular activated carbon are contained in a tank 1 having a raw water inflow pipe 2 at the upper part and a treated water outflow pipe 3 at the lower part. When the submerged bed 4 filled with plastic particles or any other granular material is used and a sedimentable granular material having a specific gravity of 1.0 or more is used, the lower part of the submerged bed 4 is supported by a supporting member 5 to In the case of using the floating granular material of less than 1.0, a porous water-permeable member 5'such as a net for preventing the floating granular material from flowing out is provided on the upper part of the immersion bed 4. An air diffuser 6 for aeration is provided under the support member 5 or the floating submerged floor, and is connected to an air blower 7.

なお、第1図示例では、原水流入管2から槽1内に流入
した原水は槽1内を下向流で流下し、処理水となって処
理水流出管3から槽1外に流出するようになっている
が、原水流入管2と処理水流出管3の上下位置を図示例
と逆にし、原水が槽1内を上向流で流下したのち処理水
となって上部から流出するようにすることもできる。
In the first illustrated example, the raw water that has flowed into the tank 1 from the raw water inflow pipe 2 flows down in the tank 1 in a downward flow, becomes treated water, and flows out of the tank 1 from the treated water outflow pipe 3. However, the upper and lower positions of the raw water inflow pipe 2 and the treated water outflow pipe 3 are reversed from the illustrated example so that the raw water flows downward in the tank 1 as treated water and then flows out from the upper part. You can also do it.

さらに、槽1の上部には、洗浄排水管8が開口され、こ
の洗浄排水管8は固液分離装置9に連なっている。固液
分離装置9としては、図示例では沈降分離槽タイプのも
のを示したが、浮上分離,膜分離,スクリーン分離,遠
心分離,過分離などの手段を採用することもできる。
固液分離装置9の分離水流出管10は洗浄用水貯槽11に連
なり、この洗浄用水貯槽11は洗浄ポンプ12を介して槽1
の下部に連なっている。
Further, a cleaning drainage pipe 8 is opened in the upper part of the tank 1, and this cleaning drainage pipe 8 is connected to a solid-liquid separation device 9. As the solid-liquid separator 9, a sedimentation tank type is shown in the illustrated example, but means such as flotation, membrane separation, screen separation, centrifugal separation, and superseparation can also be adopted.
The separated water outflow pipe 10 of the solid-liquid separation device 9 is connected to a cleaning water storage tank 11, and this cleaning water storage tank 11 is connected via a cleaning pump 12 to the tank 1
Are connected to the bottom of.

13は、洗浄排水管8に連結された高分子凝集剤注入管、
14は固液分離装置9の排泥管を示す。
13 is a polymer coagulant injection pipe connected to the washing drain pipe 8,
Reference numeral 14 denotes a sludge discharge pipe of the solid-liquid separator 9.

なお、処理水流出管3から流出する処理水を貯留する処
理水貯槽15を設け、この処理水貯槽15と固液分離装置9
の分離水流出管10又は洗浄用水貯槽11とを配管16によっ
て連結し、処理水を洗浄用水に補給するようにすること
が好ましい。
A treated water storage tank 15 for storing treated water flowing out from the treated water outflow pipe 3 is provided, and the treated water storage tank 15 and the solid-liquid separation device 9 are provided.
It is preferable that the separated water outflow pipe 10 or the cleaning water storage tank 11 is connected by a pipe 16 so that the treated water is supplied to the cleaning water.

〔考案の効果〕[Effect of device]

以上述べたように本考案によれば、次のような極めて重
要効果が得られる。
As described above, according to the present invention, the following extremely important effects can be obtained.

好気性浸漬床装置によって生産された清澄な処理水
を、浸漬床の洗浄用水として消費する必要がなく、洗
浄排水をれ自身を連続的に清澄化し、再度洗浄用水とし
て再利用する新システム構成としたので、原水BOD,SSが
高濃度の場合でも、処理水生産効率、即ち(処理水量/
原水通水量)比が悪化せず、なんら問題を生ずることな
く効果的な処理が可能である。この結果、従来、低濃度
のBOD,SSの原水しか適用できなかった好気性浸漬床装
置の適用可能な対象原水が大幅に拡大される。
It is not necessary to use the clear treated water produced by the aerobic submerged bed equipment as cleaning water for the submerged bed, the cleaning drainage is continuously clarified, and the system is reused again as cleaning water. Therefore, even if the raw water BOD, SS has a high concentration, the treated water production efficiency, that is, (the treated water amount /
The raw water flow rate) does not deteriorate, and effective treatment is possible without any problems. As a result, the target raw water applicable to the aerobic submerged bed apparatus, which has been conventionally applicable only to low-concentration BOD and SS raw water, is greatly expanded.

原水BODが高濃度の場合でも、従来のような別個の生
物処理工程を好気性浸漬床装置の前段にもける必要が
なく、SSが高濃度の場合でも、原水沈殿槽を設ける必要
もない。従って、装置建設費と設置面積が大幅に節減さ
れ、また極めて大容量の洗浄用水貯槽と洗浄排水貯槽が
不要になり、設置面積,建設費の低減効果も顕著であ
る。
Even when the raw water BOD is at a high concentration, it is not necessary to provide a separate biological treatment step before the aerobic submerged bed unit as in the conventional case, and even when the SS is at a high concentration, it is not necessary to provide a raw water settling tank. Therefore, the equipment construction cost and the installation area are significantly reduced, and an extremely large-capacity cleaning water storage tank and cleaning drainage storage tank are not required, and the installation area and construction cost are significantly reduced.

洗浄排水量は、原水流入量に比べて大幅に少量である
ため、洗浄排水を処理し、清澄な洗浄用水を得るための
固液分離装置もコンパクトなものですみ、建設費も安価
である。
Since the amount of washing wastewater is much smaller than the amount of raw water inflow, the solid-liquid separation device for treating the washing wastewater to obtain clear washing water is compact, and the construction cost is low.

洗浄排水の固液分離装置から排出される汚泥は、脱水
性が非常に良好で、そのまま新たな脱水助剤を設けるこ
となく脱水処理可能である。
The sludge discharged from the solid-liquid separation device for washing wastewater has a very good dewatering property, and can be dehydrated as it is without providing a new dewatering aid.

洗浄排水の水量が原水に加算されないので、好気性浸
漬床装置への水量負荷が軽減される(従来装置では、
洗浄排水の水量が原水流入量に加算されてしまうので、
通水負荷が大きくなる)。
Since the amount of cleaning wastewater is not added to the raw water, the load on the aerobic immersion floor device is reduced (in the conventional device,
Since the amount of washing wastewater is added to the amount of raw water inflow,
Large water flow load).

従来装置では、浸漬床の洗浄頻度(回/日)に正比
例して処理水生産効率、(処理水量/原水処理量)比が
減少してしまうが、本考案では床洗浄頻度に無関係
に、常に高い処理水生産効率を得ることできる。
In the conventional device, the treated water production efficiency and the (treated water amount / raw water treated amount) ratio decrease in direct proportion to the cleaning frequency (times / day) of the submerged bed. High treated water production efficiency can be obtained.

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

第1図は本考案の一実施例を示す縦断面図、第2図は従
来例を示す縦断面図である。 1,21…槽、2,25…原水流入管、 3,27…処理水流出管、4,22…浸漬床、 5…支持部材、5′…多孔性通水部材、 6,23…散気管、7,26…空気ブロワー、 8…洗浄排水管、9…固液分離装置、10…分離水流出
管、11…洗浄用水貯槽、12,29…洗浄ポンプ、13…高分
子凝集剤注入管、 15,28…処理水貯槽、16…配管、24…沈殿池、30…洗浄
排水槽、31…洗浄室用ブロワー、32…逆洗空気管。
FIG. 1 is a vertical sectional view showing an embodiment of the present invention, and FIG. 2 is a vertical sectional view showing a conventional example. 1,21 ... Tank, 2,25 ... Raw water inflow pipe, 3,27 ... Treated water outflow pipe, 4,22 ... Immersion bed, 5 ... Support member, 5 '... Porous water-passing member, 6,23 ... Diffuser pipe , 7,26 ... Air blower, 8 ... Wash drainage pipe, 9 ... Solid-liquid separation device, 10 ... Separation water outflow pipe, 11 ... Wash water storage tank, 12, 29 ... Wash pump, 13 ... Polymer flocculant injection pipe, 15, 28 ... Treated water storage tank, 16 ... Piping, 24 ... Sedimentation tank, 30 ... Washing drainage tank, 31 ... Washing room blower, 32 ... Backwash air pipe.

Claims (2)

【実用新案登録請求の範囲】[Scope of utility model registration request] 【請求項1】原水流入部と処理水流出部を設けた槽内に
粒状材を充填した浸漬床を設け、該浸漬床の下部
に酸素含有ガスの散気装置を配備した好気性浸漬床装
置において、前記浸漬床の洗浄排水流出路を固液分離
装置に連通し、該固液分離装置の分離水を前記浸漬床
の下部に圧送する洗浄手段を設けたことを特徴とする好
気性浸漬床装置。
1. An aerobic immersion bed apparatus in which a dipping bed filled with a granular material is provided in a tank provided with a raw water inflow section and a treated water outflow section, and an oxygen-containing gas diffuser is provided below the immersion bed. The aerobic immersion floor, wherein the cleaning drainage outflow passage of the immersion bed is connected to a solid-liquid separation device, and a cleaning means is provided for pumping the separated water of the solid-liquid separation device to the lower part of the immersion bed. apparatus.
【請求項2】前記処理水流出部から流出する処理水の一
部を前記固液分離装置の分離水に補給する補給手段を付
設した請求項1記載の好気性浸漬床装置。
2. The aerobic submerged bed apparatus according to claim 1, further comprising replenishing means for replenishing a part of the treated water flowing out from the treated water outflow portion to the separated water of the solid-liquid separation device.
JP1990023664U 1990-03-12 1990-03-12 Aerobic immersion ▲ Floor ▼ Floor equipment Expired - Fee Related JPH0642793Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1990023664U JPH0642793Y2 (en) 1990-03-12 1990-03-12 Aerobic immersion ▲ Floor ▼ Floor equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1990023664U JPH0642793Y2 (en) 1990-03-12 1990-03-12 Aerobic immersion ▲ Floor ▼ Floor equipment

Publications (2)

Publication Number Publication Date
JPH03115099U JPH03115099U (en) 1991-11-27
JPH0642793Y2 true JPH0642793Y2 (en) 1994-11-09

Family

ID=31526644

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1990023664U Expired - Fee Related JPH0642793Y2 (en) 1990-03-12 1990-03-12 Aerobic immersion ▲ Floor ▼ Floor equipment

Country Status (1)

Country Link
JP (1) JPH0642793Y2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4914286B2 (en) * 2007-04-27 2012-04-11 モリト株式会社 Ear warmer

Also Published As

Publication number Publication date
JPH03115099U (en) 1991-11-27

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