JPH0751687A - Upward current type biological filter device - Google Patents

Upward current type biological filter device

Info

Publication number
JPH0751687A
JPH0751687A JP5226617A JP22661793A JPH0751687A JP H0751687 A JPH0751687 A JP H0751687A JP 5226617 A JP5226617 A JP 5226617A JP 22661793 A JP22661793 A JP 22661793A JP H0751687 A JPH0751687 A JP H0751687A
Authority
JP
Japan
Prior art keywords
filter
grid
water
filter layer
filter bed
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
Application number
JP5226617A
Other languages
Japanese (ja)
Inventor
Mikio Kitagawa
幹夫 北川
Atsushi Watanabe
敦 渡辺
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries Ltd
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 by Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP5226617A priority Critical patent/JPH0751687A/en
Publication of JPH0751687A publication Critical patent/JPH0751687A/en
Pending legal-status Critical Current

Links

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

Abstract

PURPOSE:To drastically decrease the frequencies of backwashing the entire part of filter beds by dividing the filter beds with horizontal grid to the upper filter bed and the lower filter bed, disposing an air diffusion pipes for aeration on the grid and providing the grid with a water spraying pipes for spraying washing water downward thereunder. CONSTITUTION:The filter bed 11 of a filter tank 10 is partitioned by the grid 14 which does not allow the passage of filter media unless descending flow of, for example, 40 to 50m/hour is imparted to the lower filter bed 13 for mainly capturing SS and the upper filter bed 12 mainly decomposing BOD. The grid 14 is provided thereon with the air diffusion pipes 19 for aeration to supply oxygen and air to living thing films sticking to the filter media of the upper filter bed 12 and to enhance the activity thereof, thereby the filter bed is sufficiently provided with the function to decompose the BOD. The lower filter bed 13 for mainly capturing the SS is increased in pressure drop by the SS in a short period and, therefore, the lower filter bed is formed by lowering its bed height and decreasing the amt. of the filter media so as to be effectively backwashed by the water spraying pipes 20 disposed under the grid 14.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、濾過槽内に微生物を
付着した浮上性の濾材による濾層を設け、原水を上記濾
層に上向流で供給する上向流式生物濾過装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an upflow type biological filtration device in which a filtration layer of a buoyant filtration material having microorganisms attached is provided in a filtration tank and raw water is supplied to the filtration layer in an upward flow.

【0002】[0002]

【従来の技術】ポリプロピレンや、ウレタン樹脂等を直
径3〜10mmの球状や、不定形状に発泡成形した比重
が極めて小さい浮上性の濾材で濾過槽内に濾層を構成
し、この濾層に微生物を付着させ、原水と空気を濾層に
上向流で供給して生物濾過を行う生物濾過装置が開発さ
れている。この浮上性濾材は、発泡成形されているので
小粒径でありながら表面積が広いため、濾材に付着する
生物膜の保持量は極めて大であり、その結果、高負荷運
転が可能となり、高度の処理水を得ることができる。
又、濾材は比重が0.1以下で、浮上性を有するため、
洗浄が容易であり、濾層が捕捉したSSを濾材から剥し
て除去するのに要する洗浄用空気や、洗浄水の使用量は
低減する。
2. Description of the Related Art A filter layer is constructed in a filter tank by a floatable filter material having a very small specific gravity formed by foaming polypropylene or urethane resin into a spherical or irregular shape having a diameter of 3 to 10 mm, and microorganisms are added to this filter layer. Has been developed, and a biological filtration device has been developed for performing biological filtration by supplying raw water and air to the filter bed in an upward flow. Since this floatable filter medium has a small particle size and a large surface area because it is foam-molded, the retention amount of biofilm adhering to the filter medium is extremely large, and as a result, high load operation becomes possible and Treated water can be obtained.
Further, since the filter medium has a specific gravity of 0.1 or less and has a floating property,
It is easy to wash, and the amount of washing air and the amount of washing water required to remove the SS captured by the filter layer from the filter medium are reduced.

【0003】上記生物濾過装置では、濾過槽内の水中の
上部に通水性の上面支持板を配置し、この支持板の下に
浮上性濾材を存在させて濾層を構成し、濾材は上面支持
板から上には行けないようにし、濾過槽内の底部に空気
と、原水とを供給し、空気によって濾材に付着する微生
物を活性化し、原水が濾層中を上向流で通水する際に原
水中のBODを生物処理しながら濾過し、処理水とす
る。
In the above-mentioned biological filtration apparatus, a water-permeable upper support plate is arranged above the water in the filtration tank, and a floating filter medium is present under the support plate to form a filter layer. When it is not possible to go up from the plate, air and raw water are supplied to the bottom of the filtration tank to activate microorganisms adhering to the filter medium by the air, and when the raw water flows upward in the filter layer. The BOD in the raw water is filtered while being biologically treated to obtain treated water.

【0004】[0004]

【発明が解決しようとする課題】この濾過装置において
は、上向流する原水と、浮上する気泡とにより濾層を構
成する浮上性の濾材は上面支持板の下に密集、集結して
固定床となり、原水は濾材の間隙を空気と共に上に抜け
て行く。このため、原水中のSSや、発生した汚泥は固
定床となった濾層の底部で主に捕捉され、その底部に位
置する濾材の汚泥付着量、SSの捕捉量は増加するが、
濾層のそれよりも上の部分に位置する濾材の汚泥付着
量、SS捕捉量は極端に少ない。又、濾材の表面に付
着、生育する生物膜も固定床となった濾層の底部に位置
する濾材に主に生じ、それより上の部分の濾材に付着、
生育する生物膜量は非常に少ない。そして、濾層の底部
の圧力損失が高まると、圧力損失の低いそれよりも上の
部分までも一緒に洗浄しなければならない。要するに、
濾層の底部よりも上に位置する濾材は有効に活用されて
いないと共に、洗浄頻度も大である。このようなことか
ら、洗浄頻度を少なくするために、生物濾過装置で処理
する原水はSSが50mg/立以下の低濃度排水が適
し、それよりもSSが多い排水の場合は、前処理として
沈降分離や浮上分離を行い、含まれているSSの多くを
分離、除去しているのが現状である。
In this filtration device, the buoyant filter media forming the filter layer by the upward flowing raw water and the floating air bubbles is densely gathered under the upper support plate and fixed to the fixed bed. Then, the raw water goes up through the gap of the filter medium together with the air. Therefore, SS in the raw water and the generated sludge are mainly trapped at the bottom of the filter bed that is a fixed bed, and the sludge adhesion amount of the filter material located at the bottom and the trapped amount of SS increase,
The sludge adhesion amount and SS trapping amount of the filter medium located above the filter layer are extremely small. In addition, the biofilm that adheres to and grows on the surface of the filter medium also occurs mainly on the filter medium located at the bottom of the filter layer that has become the fixed bed, and adheres to the filter medium above it
Very few biofilms grow. Then, when the pressure loss at the bottom of the filter layer is increased, the portion above the low pressure loss must be washed together. in short,
The filter medium located above the bottom of the filter layer is not effectively utilized and the cleaning frequency is high. Therefore, in order to reduce the frequency of cleaning, low-concentration wastewater with SS of 50 mg / cubic or less is suitable as raw water to be treated by the biological filtration device, and in the case of wastewater with more SS than that, sedimentation is performed as pretreatment. At present, separation and floating separation are performed to separate and remove most of the contained SS.

【0005】[0005]

【課題を解決するための手段】本発明は上記に鑑み、開
発されたもので、濾過槽内に微生物を付着した浮上性の
濾材による濾層を設け、原水を上記濾層に上向流で供給
する上向流式生物濾過装置において、上記濾層を、濾層
中に水平に設けたグリッドにより上部濾層と、下部濾層
に区劃し、グリッド上に曝気用散気管を配設すると共
に、グリッドの下に洗浄水を下向きに散水する散水管を
設けたことを特徴とする。
DISCLOSURE OF THE INVENTION The present invention was developed in view of the above, and a filter layer is provided in the filter tank by a floatable filter material having microorganisms attached thereto, and raw water is flown upward to the filter layer. In an upflow biological filtration device for supplying, the filter layer is divided into an upper filter layer and a lower filter layer by a grid horizontally provided in the filter layer, and an aeration diffuser tube is arranged on the grid. At the same time, a sprinkling pipe for sprinkling the washing water downward is provided under the grid.

【0006】[0006]

【実施例】図示の実施例において、10は濾過槽、11
は浮上性の濾材で構成した濾層、15は濾過槽内の水中
の上部に設けた上記濾層の上面を規定する通水性の上面
支持板、16は濾過槽内の底に原水を供給する原水供給
管、17は濾過槽内の上部から処理水を取出す取出管、
18は濾過槽内に上から洗浄水を供給する洗浄水供給管
を示し、これらは従来の上向流式生物濾過装置に使用さ
れているものと同じである。濾層11中には網状、又は
格子状のグリッド14を水平に設け、濾層を層高の高い
上部濾層12と、層高の低い下部濾層13に区劃する。
そして、グリッド14上には曝気用散気管19を配設す
ると共にグリッドの下には下向きに散水する散水管20
を配設し、槽内底部の槽内液を洗浄水としてポンプP、
循環管21で散水管20に供給するようにする。
EXAMPLE In the illustrated example, 10 is a filter tank, 11
Is a filter layer composed of a floating filter material, 15 is a water-permeable upper support plate that defines the upper surface of the filter layer provided above the water in the filtration tank, and 16 supplies raw water to the bottom of the filtration tank. Raw water supply pipe, 17 is an extraction pipe for taking out treated water from the upper part in the filtration tank,
Reference numeral 18 denotes a wash water supply pipe for supplying wash water into the filtration tank from above, which are the same as those used in the conventional upflow type biological filtration device. A mesh-like or lattice-like grid 14 is horizontally provided in the filter layer 11, and the filter layer is divided into an upper filter layer 12 having a high bed height and a lower filter layer 13 having a low bed height.
An aeration diffuser tube 19 is arranged on the grid 14 and a downward sprinkler tube 20 is provided under the grid.
And a pump P using the in-tank liquid at the bottom of the tank as washing water,
The circulation pipe 21 supplies the water to the water spray pipe 20.

【0007】濾層11を構成する濾材は、比重が0.0
3kg/立(乾燥状態)で、平均粒径3mmの発泡スチ
ロール製の細粒であり、上面支持板15には網目の大き
さが2mm以下の網又はストレーナーを用い、上面支持
板15から濾材が流出しないようにする。グリッド14
は、網又は格子目の大きさが30〜50mmの網又は格
子を用いる。濾材に通水線速度として40〜50m/時
の下降流の流速を与えたときや、曝気用空気の供給下で
通水線速度2〜10m/時で上向流の通水しているとき
には、水流や空気の存在により濾材の流動性が高まるた
め、グリッドの網目又は格子目を通して濾材が移動する
が、濾層内の槽内液を排出し濾材を水から分離したとき
には、グリッド14表面で濾材がブリッジを形成し濾材
は移動しない。実験的設備として直径370mm、高さ
3500mmの透明カラムを濾過槽に使用し、グリッド
14上に層高2500mmの上部濾層12と、グリッド
の下に層高50mmの下部濾層13を設けた。
The filter medium constituting the filter layer 11 has a specific gravity of 0.0
3 kg / standing (dry state), fine particles made of styrofoam with an average particle diameter of 3 mm, and a mesh or strainer having a mesh size of 2 mm or less is used as the upper support plate 15, and the filter medium flows out from the upper support plate 15. Try not to. Grid 14
Is a mesh or grid having a mesh or grid size of 30 to 50 mm. When a downward flow velocity of 40 to 50 m / hr is applied to the filter medium as a linear velocity, or when upward flow of water is performed at a linear flow velocity of 2 to 10 m / hr while supplying aeration air. Since the flowability of the filter medium increases due to the presence of water flow and air, the filter medium moves through the mesh or grid of the grid, but when the liquid in the tank in the filter layer is discharged and the filter medium is separated from water, the The filter medium forms a bridge and the filter medium does not move. As the experimental equipment, a transparent column having a diameter of 370 mm and a height of 3500 mm was used as a filtration tank, and an upper filter layer 12 having a layer height of 2500 mm was provided on a grid 14 and a lower filter layer 13 having a layer height of 50 mm was provided below the grid.

【0008】運転を行うには、その当初に下水処理場の
活性汚泥の余剰汚泥を濾材の量に対し適当量、濾過槽内
に投入し、グリッド上の曝気用散気管19に酸素ないし
空気を供給して汚泥を構成する微生物を活性化して汚泥
を濾材に膜状に付着させ、濾材に充分な量の生物膜が付
着したら曝気用散気管19からの酸素ないし空気の供給
を続けたまゝで槽内底部に原水供給管16から原水を供
給し、濾層11中を上向流させる。これによって原水は
下部濾層13中を上向流する際に主にSSを捕捉されて
除かれ、次いでグリッド14を通過して上部濾層12中
を上向流する際に濾材に付着して生物膜でBODを生物
処理され、処理水となって取出管17から溢流する。
尚、原水の上向流の通水線速度(LV)は2〜10m/
時、曝気用散気管19からの酸素ないし空気の通気線速
度は8〜20m/時である。
To perform the operation, an excess amount of activated sludge in the sewage treatment plant is initially charged into the filter tank in an appropriate amount with respect to the amount of the filter medium, and oxygen or air is supplied to the aeration diffuser 19 on the grid. When the sludge is supplied to activate the microorganisms that compose the sludge to attach the sludge to the filter medium in a film form, and if a sufficient amount of biofilm is attached to the filter medium, continue supplying oxygen or air from the aeration diffuser tube 19. Raw water is supplied from the raw water supply pipe 16 to the bottom of the tank to cause an upward flow in the filter layer 11. As a result, the raw water is mainly trapped and removed by SS when flowing upward in the lower filter layer 13, and then adheres to the filter medium when flowing upward through the grid 14 in the upper filter layer 12. BOD is biologically treated with a biofilm and becomes treated water and overflows from the extraction pipe 17.
The upward flow rate of raw water (LV) is 2-10m /
At this time, the aeration linear velocity of oxygen or air from the aeration diffuser 19 is 8 to 20 m / hour.

【0009】こうして運転を行うと、捕捉したSSによ
り先ず下部濾層13の圧力損失が高まる。その圧力損失
が水柱2000〜3000mmに達したら、原水と曝気
用空気の供給を停め、槽底のドレン管22より濾過槽内
液をグリッド14の高さまで通水線速度20m/時以下
の流速で排水する。その後循環ポンプPを運転し、槽内
液を循環管21を経て散水管20に供給し、下部濾槽中
に通水線速度40〜50m/時で下降流させて下部濾層
を形成する構成する濾材を展開率5〜10%で展開・流
動させ、濾材に付着するSSやBOD成分を濾材から剥
離する。この行程を2〜10分間行ったら槽底のドレン
管22から槽内液を、剥離したSS等と共に排水する。
そして、洗浄水供給管18からグリッド14の高さまで
洗浄水(処理水、又は工水)で水張りを行ったのち運転
を再開する。下部濾層の逆洗所要時間は5〜15分間で
ある。この逆洗時には、前もって槽内液をグリッド14
の高さまで排出してあるため、グリッド14上部の上部
濾層12の濾材は、グリッド上部でブリッジを形成して
下部濾層13と混合することはない。尚、逆洗開始時
の、グリッド14の高さまで槽内液を排出する線速度を
40m/時以上に高めると、上部濾層がグリッドの網目
や格子目を通過して下部濾層と混合する恐れがある。こ
の下部濾層の逆洗は、圧力損失が水柱2000〜300
0mmに達した都度行う。尚、槽底部に洗浄用散気管2
3を設け、散水管20からの下向き散水時にこの散気管
23から空気を連続的、又は間欠的に噴出させると洗浄
効果を高めることができて好ましい。
When operated in this manner, the trapped SS first increases the pressure loss of the lower filter layer 13. When the pressure loss reaches 2000-3000 mm of water column, the supply of raw water and aeration air is stopped, and the liquid in the filtration tank is passed through the drain pipe 22 at the bottom of the tank to the height of the grid 14 at a flow velocity of 20 m / hr or less. Drain. After that, the circulation pump P is operated, the liquid in the tank is supplied to the water sprinkling pipe 20 through the circulation pipe 21, and the liquid is made to flow downward into the lower filter tank at a water flow linear velocity of 40 to 50 m / hour to form a lower filter layer. The filter material is spread and fluidized at a spreading rate of 5 to 10%, and the SS and BOD components adhering to the filter material are separated from the filter material. After performing this step for 2 to 10 minutes, the in-tank liquid is drained from the drain pipe 22 at the bottom of the tank together with the separated SS and the like.
Then, after the flush water is filled from the flush water supply pipe 18 to the height of the grid 14 with flush water (treated water or industrial water), the operation is restarted. The time required for backwashing the lower filter layer is 5 to 15 minutes. At the time of this backwashing, the liquid in the tank is gridded in advance.
Since it has been discharged to a height of 1, the filter medium of the upper filter layer 12 above the grid 14 does not mix with the lower filter layer 13 by forming a bridge at the upper part of the grid. When the linear velocity for discharging the liquid in the tank to the height of the grid 14 at the start of backwashing is increased to 40 m / hour or more, the upper filter layer passes through the mesh or grid of the grid and is mixed with the lower filter layer. There is a fear. This backwashing of the lower filter layer has a pressure loss of 2000-300 water column.
Perform every time it reaches 0 mm. In addition, the air diffuser 2 for cleaning is installed at the bottom of the tank.
3 is provided, and it is preferable that air is continuously or intermittently ejected from the air diffusing pipe 23 at the time of downward water sprinkling from the water sprinkling pipe 20 because the cleaning effect can be enhanced.

【0010】原水中の、主にBODを分解処理する上部
濾層12の圧力損失が高まり、それが水柱2000〜3
000mmに達したら上部濾層、及び下部濾層の全体を
逆洗する。それには原水と曝気用空気の供給を停め、洗
浄水供給管18から洗浄水(処理水、又は工水)を濾過
槽10に上から供給し、上部濾層及び下部濾層中に下向
流で通水しながら、洗浄排水をドレン管22で排出す
る。洗浄水の下向流の通水線速度は40〜50m/時と
し、これによって上下両濾層の濾材はグリッド14の網
目又は格子目を通して5〜10%の展開率で展開、流動
させ、濾層に捕捉されたSS、濾材に過剰に付着した生
物膜を剥離し、洗浄排水と一緒に排出する。この場合
も、グリッド14上の曝気用散気管19、及び槽底の洗
浄用散気管23から空気を連続的、又は間欠的に噴出す
ることで洗浄効果は高まる。洗浄水量は、上下両濾層の
全濾材容量の1.5〜3倍量である。洗浄工程が終った
ら、洗浄水供給管18からの水で水張り工程を行ったの
ち運転を再開する。この逆洗の所要時間は20〜40分
間程度である。
The pressure loss of the upper filter layer 12 in the raw water, which mainly decomposes BOD, is increased, which is caused by the water column 2000-3.
When reaching 000 mm, the entire upper filter layer and lower filter layer are backwashed. For this purpose, supply of raw water and aeration air is stopped, and wash water (treated water or industrial water) is supplied from above to the filter tank 10 through the wash water supply pipe 18 and flows downward into the upper filter layer and the lower filter layer. The drainage water is drained through the drain pipe 22 while passing water through. The water flow linear velocity of the downward flow of the washing water is 40 to 50 m / hour, whereby the filter media of the upper and lower filter layers are developed and flowed through the mesh or grid of the grid 14 at a development rate of 5 to 10%, and then filtered. The SS trapped in the layer and the biofilm excessively attached to the filter medium are peeled off and discharged together with the cleaning drainage. In this case as well, the cleaning effect is enhanced by continuously or intermittently ejecting air from the aeration diffuser 19 on the grid 14 and the cleaning diffuser 23 on the bottom of the tank. The amount of washing water is 1.5 to 3 times the total volume of the filter material in both the upper and lower filter layers. After the cleaning process is completed, the water is supplied from the cleaning water supply pipe 18 to perform a water filling process, and then the operation is restarted. The time required for this backwash is about 20 to 40 minutes.

【0011】下部濾層の逆洗時、及び上下両濾層の逆洗
時、ドレン管から排出される洗浄排水にはSS以外に、
BODの一部が汚泥や、SSに吸着された濃縮状態で含
まれている。この洗浄排水を脱水処理すると、発生する
脱水濾液は汚泥やSSから溶出したBOD成分を多く含
む。このため、脱水濾液を生物濾過装置に供給、通水す
ると、生物濾過装置の負荷量を高めることになる。そこ
で、洗浄排水を脱水処理する場合は、その前に曝気槽2
4に供給して汚泥やSS中のBOD成分を分解し、それ
から分離濃縮槽25で濃縮し、濃縮したものを脱水機2
6に供給し、脱水することが好ましい。
When backwashing the lower filter layer and backwashing both the upper and lower filter layers, in addition to SS, the cleaning drainage discharged from the drain pipe is
A part of BOD is contained in a sludge or in a concentrated state adsorbed on SS. When this washing wastewater is dehydrated, the dehydrated filtrate generated contains a large amount of BOD components eluted from sludge and SS. Therefore, when the dehydrated filtrate is supplied to and passed through the biological filtration device, the load on the biological filtration device is increased. Therefore, before dewatering the cleaning wastewater, the aeration tank 2
4 to decompose BOD components in sludge and SS, and then concentrate them in a separation / concentration tank 25.
It is preferable to supply to No. 6 and dehydrate.

【0012】逆洗時に下部濾層13の濾材がドレン管2
2から流出するのを防止するため、下部濾層12の下面
に濾材が通過しない目開きの孔、スリットなどを有する
通水性の下面支持部材を設けるか、ドレン管に下部濾層
の下面よりも立ち上り部を図示の如く設ける。
During backwashing, the filter material of the lower filter layer 13 is the drain pipe 2
In order to prevent the water from flowing out from 2, the lower surface of the lower filter layer 12 is provided with a water-permeable lower surface supporting member having openings, slits, etc. through which the filter medium does not pass, or the drain pipe is provided with a lower surface than the lower surface of the lower filter layer. The rising portion is provided as shown.

【0013】この実施例では下部濾層を逆洗するために
散水管20から下向きに噴出する水として槽内液を循環
使用したが、これに限らず、処理水や工水を使用するこ
ともできる。その場合は処理水又は工水の供給管を散水
管20に接続し、散水管20から処理水又は工水を散水
するときは槽内液をドレン管22から排水する。
In this embodiment, in order to backwash the lower filter layer, the in-tank liquid is circulated and used as the water jetted downward from the sprinkling pipe 20, but not limited to this, treated water or industrial water may be used. it can. In that case, the supply pipe of the treated water or the industrial water is connected to the sprinkler pipe 20, and when the treated water or the industrial water is sprinkled from the sprinkler pipe 20, the tank liquid is drained from the drain pipe 22.

【0014】[0014]

【発明の効果】以上で明らかなように、本発明では濾層
11を、通水線速度として40〜50m/時の下降流を
与えない限り濾材を通過させることがないグリッド14
により主としてSSの捕捉を主に行う下部濾層13と、
主にBODを分解する上部濾層12に仕切り、グリッド
上に曝気用散気管19を設け、該層の濾材に付着する生
物膜に酸素ないし空気を供給して活性を高め、BOD分
解機能を充分に保たせた。そして、SSの捕捉を主に行
う下部濾層は短期間で圧力損失が高まるため、層高を低
くして濾材の量を少なくし、グリッドの下に設けた散水
管20によって効果的に逆洗できるようにした。これに
より捕捉したSSで圧力損失が高まったら、濾層全体を
逆洗するのではなく下部濾層のみを逆洗すればよく、濾
層全体を逆洗する頻度は大幅に減少する。
As is apparent from the above, according to the present invention, the filter layer 11 does not allow the filter medium to pass therethrough unless a downward flow of 40 to 50 m / hour as a water-passing linear velocity is applied.
By the lower filter layer 13 which mainly captures SS,
The upper filter layer 12 that mainly decomposes BOD is partitioned, and an aeration diffuser tube 19 is provided on the grid, and oxygen or air is supplied to the biofilm adhering to the filter material of the layer to enhance the activity, and the BOD decomposition function is sufficiently achieved. I kept it. Since the lower filter layer, which mainly captures SS, has a high pressure loss in a short period of time, the layer height is reduced to reduce the amount of the filter medium, and backwashing is effectively performed by the water spray pipe 20 provided under the grid. I made it possible. When the pressure loss increases due to the captured SS, only the lower filter layer needs to be backwashed instead of backwashing the entire filter layer, and the frequency of backwashing the entire filter layer is greatly reduced.

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

【図1】本発明による上向流式生物濾過装置の一実施例
のフローシートである。
FIG. 1 is a flow sheet of an embodiment of an upflow type biological filtration device according to the present invention.

【符号の説明】 10 濾過槽 11 濾層 12 上部濾層 13 下部濾層 14 グリッド 15 上面支持板 16 原水供給管 17 処理水取出管 18 洗浄水供給管 19 曝気用散気管 20 散水管[Explanation of Codes] 10 Filter Tank 11 Filter Layer 12 Upper Filter Layer 13 Lower Filter Layer 14 Grid 15 Top Support Plate 16 Raw Water Supply Pipe 17 Treated Water Extraction Pipe 18 Wash Water Supply Pipe 19 Aeration Diffuser 20 Water Sprinkler

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 // B01D 24/02 8925−4D B01D 29/08 540 A 23/10 C ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location // B01D 24/02 8925-4D B01D 29/08 540 A 23/10 C

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 濾過槽内に微生物を付着した浮上性の濾
材による濾層を設け、原水を上記濾層に上向流で供給す
る上向流式生物濾過装置において、上記濾層を、濾層中
に水平に設けたグリッドにより上部濾層と、低い下部濾
層に区劃し、グリッド上に曝気用散気管を配設すると共
に、グリッドの下に洗浄水を下向きに散水する散水管を
設けたことを特徴とする上向流式生物濾過装置。
1. An upflow type biological filtration device in which a filtration layer of a buoyant filter material having microorganisms attached thereto is provided in a filtration tank, and raw water is supplied to the filtration layer in an upward flow. A horizontal grid in the layer separates the upper filter layer and the lower lower filter layer, and an aeration pipe for aeration is arranged on the grid, and a sprinkler pipe for spraying washing water downward is also provided under the grid. An upflow type biological filtration device characterized by being provided.
JP5226617A 1993-08-20 1993-08-20 Upward current type biological filter device Pending JPH0751687A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5226617A JPH0751687A (en) 1993-08-20 1993-08-20 Upward current type biological filter device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5226617A JPH0751687A (en) 1993-08-20 1993-08-20 Upward current type biological filter device

Publications (1)

Publication Number Publication Date
JPH0751687A true JPH0751687A (en) 1995-02-28

Family

ID=16848015

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5226617A Pending JPH0751687A (en) 1993-08-20 1993-08-20 Upward current type biological filter device

Country Status (1)

Country Link
JP (1) JPH0751687A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08132095A (en) * 1994-11-04 1996-05-28 Kurita Water Ind Ltd Water treating device
US6676254B2 (en) 2000-12-21 2004-01-13 Canon Kabushiki Kaisha Recording method, ink cartridge, printing device and information recording apparatus
US7407537B2 (en) 2004-06-18 2008-08-05 Brother Kogyo Kabushiki Kaisha Ink set for ink-jet recording, method for producing the same, and the ink-jet printer
JP4922763B2 (en) * 2003-08-04 2012-04-25 スティーブン・エイチ・シュワルツコプフ Liquid filtration apparatus and method with super-floating filtration particles
JP2014509940A (en) * 2011-04-04 2014-04-24 ヴェオリア・ウォーター・ソリューションズ・アンド・テクノロジーズ・サポート Improved biological wastewater purification reactor and method
CN104671462A (en) * 2015-02-02 2015-06-03 北京金控自动化技术有限公司 Sewage treatment energy saving control method and control system based on bivariate two-dimensional table
CN109704511A (en) * 2018-12-25 2019-05-03 湖南恒凯环保科技投资有限公司 A kind of method high-performance bio degradation filtration reactor and handle black and odorous water with it

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08132095A (en) * 1994-11-04 1996-05-28 Kurita Water Ind Ltd Water treating device
US6676254B2 (en) 2000-12-21 2004-01-13 Canon Kabushiki Kaisha Recording method, ink cartridge, printing device and information recording apparatus
US7185978B2 (en) 2000-12-21 2007-03-06 Canon Kabushiki Kaisha Recording method, ink cartridge, printing device and information recording apparatus
JP4922763B2 (en) * 2003-08-04 2012-04-25 スティーブン・エイチ・シュワルツコプフ Liquid filtration apparatus and method with super-floating filtration particles
US7407537B2 (en) 2004-06-18 2008-08-05 Brother Kogyo Kabushiki Kaisha Ink set for ink-jet recording, method for producing the same, and the ink-jet printer
JP2014509940A (en) * 2011-04-04 2014-04-24 ヴェオリア・ウォーター・ソリューションズ・アンド・テクノロジーズ・サポート Improved biological wastewater purification reactor and method
CN104671462A (en) * 2015-02-02 2015-06-03 北京金控自动化技术有限公司 Sewage treatment energy saving control method and control system based on bivariate two-dimensional table
CN109704511A (en) * 2018-12-25 2019-05-03 湖南恒凯环保科技投资有限公司 A kind of method high-performance bio degradation filtration reactor and handle black and odorous water with it

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