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JPH04250900A - Biological treating device - Google Patents

Biological treating device

Info

Publication number
JPH04250900A
JPH04250900A JP3011527A JP1152791A JPH04250900A JP H04250900 A JPH04250900 A JP H04250900A JP 3011527 A JP3011527 A JP 3011527A JP 1152791 A JP1152791 A JP 1152791A JP H04250900 A JPH04250900 A JP H04250900A
Authority
JP
Japan
Prior art keywords
water
tower
treated
filtration
fixed 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
JP3011527A
Other languages
Japanese (ja)
Inventor
Yonekichi Tanaka
田中 米吉
Masahiro Kawabata
雅博 川端
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.)
Organo Corp
Original Assignee
Organo Corp
Japan Organo Co 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 Organo Corp, Japan Organo Co Ltd filed Critical Organo Corp
Priority to JP3011527A priority Critical patent/JPH04250900A/en
Publication of JPH04250900A publication Critical patent/JPH04250900A/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

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Filtration Of Liquid (AREA)

Abstract

PURPOSE:To provide the biological treating device which allows the reduction of the size over the entire part of the device including a pollutant separating device, efficiently yields the clean treated water contg. suspended solids at a lower ratio and facilitates and maintenance. CONSTITUTION:The upper part of a fixed bed contact oxidation column 1 of a type open to the atm. copnstituted by packing materials 3, such as crushed stone, Rasching rings and hollow cylindrical nets, into the inside and the upper part of a filter column whcih is packed with erected long fiber bundles 11 consisting of the assemblies of the extremely fine monofibers in the entire part of the column and has extremely low fluid resistance are allowed to communicate with a connecting pipe 10. The water to be treated contg. the org. matter supplied to the lower part of the fixed bed contact oxidation column 1 by a supply pump 8 is passed in ascending flow in this column and is subjected to a biolongical treatment under an arm. pressure. This treated water is then introduced into the upper part of the filter column 9 via by a water level difference the connecting pipe 10. This treated water is passed in the descending flow from the top end toward the bottom end of the long fiber bundles 11 and is filtered by a gravitational system, by which the org. matter in the water to be treated is removed.

Description

【発明の詳細な説明】[Detailed description of the invention]

【0001】0001

【産業上の利用分野】本発明は下水や、食品工場、紙パ
ルプ工場等の工場から排出される廃水等の、有機物を含
む廃水(有機性廃水)を大気圧下において、好気性微生
物を着生させるための充填材層を有する固定床接触酸化
塔と長繊維束を濾材として用いる濾過塔に順次通水する
ことにより、有機性廃水中のBODあるいはCODおよ
び懸濁物質(SS)を除去する生物処理装置に関するも
のである。
[Industrial Application Field] The present invention is a method for treating wastewater containing organic matter (organic wastewater), such as sewage and wastewater discharged from factories such as food factories and pulp and paper factories, under atmospheric pressure to attract aerobic microorganisms. BOD or COD and suspended solids (SS) in organic wastewater are removed by sequentially passing water through a fixed-bed catalytic oxidation tower having a bed of packing material for organic wastewater generation and a filtration tower using long fiber bundles as filter media. This relates to biological treatment equipment.

【0002】0002

【従来の技術】近年において有機性廃水の処理にあたり
、標準型活性汚泥処理装置に替わって比較的運転管理が
容易な接触酸化塔が用いられるようになってきた。当該
接触酸化塔の中に、塔内に好気性微生物を着生させた充
填材の層を形成し、当該充填材層の下部より被処理水を
上昇流で流入させるとともに空気等の酸素含有ガスを導
入して生物処理を行う、いわゆる固定床接触酸化塔があ
る。
BACKGROUND OF THE INVENTION In recent years, in the treatment of organic wastewater, catalytic oxidation towers, which are relatively easy to operate and manage, have been used in place of standard activated sludge treatment equipment. A layer of packing material in which aerobic microorganisms are grown is formed in the contact oxidation tower, and the water to be treated flows in an upward flow from the bottom of the packing material layer, and oxygen-containing gas such as air is introduced into the tower. There is a so-called fixed bed catalytic oxidation tower that performs biological treatment by introducing

【0003】このような固定床接触酸化塔は、通常塔上
部を大気に開放した状態で、すなわち大気圧下で生物処
理を行うが、当該固定床接触酸化塔の処理水中には前記
充填材層から剥離した余剰の好気性微生物等のSSが比
較的多量に含まれており、したがって、このSSを除去
するために濁質分離装置が必要である。そして、当該濁
質分離装置としては、一般的に沈殿分離槽が用いられる
が、より清澄な処理水を得たい場合は砂あるいはアンス
ラサイト等の粒状濾材を充填した濾過塔が用いられるこ
ともある。
Such a fixed bed catalytic oxidation tower usually performs biological treatment with the upper part of the tower open to the atmosphere, that is, under atmospheric pressure. It contains a relatively large amount of SS such as excess aerobic microorganisms separated from the water, and therefore a turbidity separator is required to remove this SS. A sedimentation separation tank is generally used as the turbidity separation device, but if clearer treated water is desired, a filtration tower filled with granular filter media such as sand or anthracite may be used. .

【0004】0004

【発明が解決しようとする問題点】しかしながら、濁質
分離装置として沈殿分離槽を用いる場合は、広大な設置
面積を必要とするという問題点があり、また濁質分離装
置として砂等の粒状濾材を充填した濾過塔を用いる場合
は、微細なSSまで除去しようとして濾材の粒径を小さ
くすると濾過速度を速くすることができないので装置の
小型化が望めないという問題があり、逆に濾過速度を速
くしようとして濾材の粒径を大きくすると、微細なSS
を捕捉するのが困難となって清澄な濾過水が得られなく
なるという問題があった。
[Problems to be Solved by the Invention] However, when a sedimentation separation tank is used as a turbidity separation device, there is a problem that a vast installation area is required. When using a filtration column filled with SS, there is a problem that if the particle size of the filter medium is reduced in an attempt to remove even the finest SS, the filtration speed cannot be increased, so it is not possible to downsize the device. If you increase the particle size of the filter medium to speed it up, fine SS
There was a problem in that it became difficult to capture the water, making it impossible to obtain clear filtered water.

【0005】本発明は上記従来技術の問題点を解決する
ものであり、濁質分離装置を含めた装置全体の小型化が
図れるとともにSS含有量の少ない清澄な処理水を効率
よく得ることができ、しかも運転管理が極めて容易な生
物処理装置を提供することを目的とするものである。
[0005] The present invention solves the problems of the prior art described above, and makes it possible to miniaturize the entire device including the turbidity separator, and to efficiently obtain clear treated water with a low SS content. Moreover, it is an object of the present invention to provide a biological treatment device that is extremely easy to operate and manage.

【0006】[0006]

【問題点を解決するための手段】上記目的を達成するた
めになされた本発明は、好気性微生物を着生させるため
の充填材層を有する大気開放型の固定床接触酸化塔の下
方部に、供給ポンプを有する被処理水流入管の一端を連
通し、また当該固定床接触酸化塔の上方部に接続管の一
端を連通するとともに当該接続管の他端を塔内全体に長
繊維束を立設した大気開放型の濾過塔の上方部に連通し
、更に当該濾過塔の下方部に濾過水流出管の一端を連通
してなり、有機物を含む被処理水を前記供給ポンプによ
って固定床接触酸化塔内に上昇流で流して大気圧下で生
物処理するとともに、生物処理を受けた固定床接触酸化
塔の処理水を接続管を介して水位差によって前記濾過塔
の上方部に導入し、当該処理水を濾過塔内に下降流で流
して重力式に濾過することを特徴とする生物処理装置で
ある。
[Means for Solving the Problems] The present invention has been made to achieve the above object, and the present invention is directed to a fixed bed catalytic oxidation tower, which is open to the atmosphere, in the lower part thereof, and which has a packing layer for attaching aerobic microorganisms. , one end of the water inflow pipe having a supply pump is connected, and one end of the connecting pipe is connected to the upper part of the fixed bed catalytic oxidation tower, and the other end of the connecting pipe is connected to a long fiber bundle throughout the tower. One end of the filtrate outflow pipe is connected to the upper part of the filtration tower which is open to the atmosphere, and one end of the filtrate water outlet pipe is connected to the lower part of the filtration tower. At the same time, the treated water from the fixed-bed catalytic oxidation tower is introduced into the upper part of the filtration tower via a connecting pipe according to the water level difference, and the water is biologically treated under atmospheric pressure by flowing upward into the tower. This biological treatment device is characterized in that treated water flows downward into a filtration tower and is filtered by gravity.

【0007】以下に本発明を図面に基づいて詳細に説明
する。図1は本発明の実施態様の一例を示すフロー説明
図であり、図中1は生物処理を大気圧下で行うように上
部が開放状態となっている固定床接触酸化塔である。当
該固定床接触酸化塔1は下方部に透水性の支持床2を配
し、その上部に砂利、砕石、多孔性セラミック、ラシヒ
リング、テラレットパッキン、中空筒状ネット、プラス
チック網様体、ハニカムチューブ等の充填材3を充填す
るとともに、支持床2の下部に、空気流入管5が接続さ
れた空気用ディストリビュータ4と、被処理水流入管7
が接続された水用ディストリビュータ6とをそれぞれ付
設し、また被処理水流入管7には被処理水を固定床接触
酸化塔1内に供給するための供給ポンプ8を付設する。
[0007] The present invention will be explained in detail below based on the drawings. FIG. 1 is a flow explanatory diagram showing an example of an embodiment of the present invention, and numeral 1 in the figure is a fixed bed catalytic oxidation tower whose top is open so that biological treatment can be carried out under atmospheric pressure. The fixed bed catalytic oxidation tower 1 has a water-permeable support bed 2 in the lower part, and the upper part has gravel, crushed stone, porous ceramic, Raschig ring, Terraret packing, hollow cylindrical net, plastic mesh, and honeycomb tube. At the same time, an air distributor 4 to which an air inflow pipe 5 is connected and a water inflow pipe 7 to be treated are installed at the bottom of the support bed 2.
A water distributor 6 to which a water distributor 6 is connected is attached, and a feed pump 8 for supplying the treated water into the fixed bed catalytic oxidation tower 1 is attached to the treated water inflow pipe 7.

【0008】上記構成の固定床接触酸化塔1においては
、空気流入管5を介して空気用ディストリビュータ4か
ら空気等の酸素含有ガスを気泡状にして均等に流出させ
ながら、被処理水流入管7を介して水用ディストリビュ
ータ6から被処理水を上昇流で流入し、充填材3の表面
に着生させた好気性微生物の働きにより被処理水中のB
OD(あるいはCOD)成分を生物学的に酸化処理し、
生物処理を受けた処理水を当該固定床接触酸化塔1の上
方部に連通した後述する接続管10から取り出すもので
ある。
In the fixed bed catalytic oxidation tower 1 having the above structure, the water to be treated inflow pipe 7 is made to flow through the water inflow pipe 7 while the oxygen-containing gas such as air is made into bubbles and uniformly flows out from the air distributor 4 through the air inflow pipe 5. The water to be treated flows upward from the water distributor 6 through the filter, and the B in the water is absorbed by the action of aerobic microorganisms grown on the surface of the filler 3
Biologically oxidizes OD (or COD) components,
Treated water that has undergone biological treatment is taken out from a connecting pipe 10, which will be described later, and which communicates with the upper part of the fixed bed catalytic oxidation tower 1.

【0009】前記固定床接触酸化塔1の後段に大気開放
型の濾過塔9を設置し、当該濾過塔9の上方部と固定床
接触酸化塔1の上方部とを、固定床接触酸化塔1の処理
水を水位差によって濾過塔9内に導入できるように接続
管10で連通する。
A filtration tower 9 open to the atmosphere is installed downstream of the fixed bed catalytic oxidation tower 1, and the upper part of the filtration tower 9 and the upper part of the fixed bed catalytic oxidation tower 1 are connected to each other. The treated water is communicated with the filter tower 9 through a connecting pipe 10 so that it can be introduced into the filter tower 9 depending on the water level difference.

【0010】当該濾過塔9の内部には、例えばアクリル
繊維、ポリエステル繊維、ポリアミド繊維等の合成繊維
からなる長さ0.4〜3.0m、太さ10〜100μ、
好ましくは20〜45μの極細の単繊維の集合体である
長繊維束11が、充填率30〜150Kg/m2 、好
ましくは50〜75Kg/m2 の割合で、塔下部に付
設した透水性の支持体12に固定されており、前記接続
管10を介して水位差によって流入する固定床接触酸化
塔1の処理水を、長繊維束11の上端から下端に向かっ
て下降流で通水して重力式に濾過する構成となっている
[0010] Inside the filter tower 9, there is a fiber having a length of 0.4 to 3.0 m and a thickness of 10 to 100 μm, which is made of synthetic fibers such as acrylic fibers, polyester fibers, and polyamide fibers.
Long fiber bundles 11, which are preferably aggregates of ultrafine single fibers with a diameter of 20 to 45μ, are attached to a water-permeable support attached to the lower part of the tower at a filling rate of 30 to 150Kg/m2, preferably 50 to 75Kg/m2. 12, and the treated water of the fixed bed catalytic oxidation tower 1, which flows in through the connecting pipe 10 depending on the water level difference, is passed in a downward flow from the upper end of the long fiber bundle 11 toward the lower end to form a gravity-type oxidation tower. It is configured to filter to.

【0011】なお、図中符号13は被処理水貯槽、14
、15はそれぞれ固定床接触酸化塔1の上部および濾過
塔9の上部に接続した洗浄排水管、16は濾過塔9の下
部に接続した濾過水流出管、17は同じく濾過塔9の下
部に接続した洗浄用水管、18は当該洗浄用水管17に
分岐接続した空気流入管、19は濾過水貯槽を示してお
り、また20〜23はそれぞれ弁を示している。
[0011] In the figure, reference numeral 13 indicates a water storage tank to be treated, and 14
, 15 are washing drain pipes connected to the upper part of the fixed bed catalytic oxidation tower 1 and the upper part of the filtration tower 9, 16 is a filtrate water outflow pipe connected to the lower part of the filtration tower 9, and 17 is also connected to the lower part of the filtration tower 9. 18 is an air inflow pipe branched and connected to the washing water pipe 17, 19 is a filtered water storage tank, and 20 to 23 are valves, respectively.

【0012】0012

【作用】次に図1を用いて本発明の操作を説明する。ま
ず、弁22、弁23を閉じ、供給ポンプ8を駆動して被
処理水貯槽13内の有機物を含む被処理水を被処理水流
入管7、弁20および水用ディストリビュータ6を介し
て固定床接触酸化塔1の下部より流入させるとともに、
酸化用の空気を空気流入管5および空気用ディストリビ
ュータ4を介して、微細な気泡状として流入させる。な
お、空気の替わりに、空気を気体選択透過膜あるいはモ
レキュラーシーブ等で処理して酸素濃度を高めた酸素富
化空気や、純酸素等の酸素含有ガスを固定床接触酸化塔
1内に流入させてもよい。
[Operation] Next, the operation of the present invention will be explained using FIG. First, the valves 22 and 23 are closed, the supply pump 8 is driven, and the water to be treated containing organic matter in the water storage tank 13 is brought into contact with the fixed bed via the water inlet pipe 7, the valve 20, and the water distributor 6. While flowing from the lower part of the oxidation tower 1,
Oxidizing air is introduced in the form of fine bubbles through the air inlet pipe 5 and the air distributor 4. In addition, instead of air, oxygen-enriched air whose oxygen concentration is increased by treating the air with a gas selective permeation membrane or molecular sieve, or an oxygen-containing gas such as pure oxygen is flowed into the fixed bed catalytic oxidation tower 1. It's okay.

【0013】流入した被処理水は、気泡状の空気ととも
に固定床接触酸化塔1内を上昇流で流れ、この間に好気
性微生物が着生した充填材3の層と大気圧下において接
触する。当該接触により、被処理水中に含まれている有
機物を好気性微生物の働きによって生物酸化することが
でき、BOD濃度の低下した処理水を固定床接触酸化塔
1の上部から得ることができる。
The inflowing water to be treated flows upward through the fixed bed catalytic oxidation tower 1 together with air bubbles, during which time it comes into contact with the layer of the packing material 3 on which aerobic microorganisms have grown under atmospheric pressure. Through this contact, organic matter contained in the water to be treated can be biooxidized by the action of aerobic microorganisms, and treated water with a reduced BOD concentration can be obtained from the upper part of the fixed bed catalytic oxidation tower 1.

【0014】得られる処理水は充填材3から剥離した余
剰の好気性微生物等の濁質を多量に含んでいるので、当
該処理水を接続管10を介して大気開放型の濾過塔9内
に導入するが、当該処理水の濾過塔9内への導入は固定
床接触酸化塔1と濾過塔9との水位差によって行われ、
したがって処理水を移送するためのポンプは必要ない。
Since the resulting treated water contains a large amount of suspended solids such as excess aerobic microorganisms that have separated from the filler 3, the treated water is passed through the connecting pipe 10 into the filtration tower 9 which is open to the atmosphere. The treated water is introduced into the filtration tower 9 by the water level difference between the fixed bed catalytic oxidation tower 1 and the filtration tower 9,
Therefore, no pump is required to transfer the treated water.

【0015】当該濾過塔9内には、前述のごとく長さが
例えば0.4〜3.0m、太さが10〜100μの単繊
維の集合体からなる長繊維束11が塔内部全体に立設さ
れている。濾過塔9内に流入した前記処理水は、当該長
繊維束11の上端から下端に向かって重力によって流下
し、この間に長繊維束11で形成される空隙部で、前記
処理水中に含まれているSSが捕捉され、濾過水は透水
性の支持体12を介して濾過水流出管16から流出し、
濾過水貯槽19に入る。
Inside the filtration tower 9, as mentioned above, a long fiber bundle 11 consisting of an aggregate of single fibers having a length of, for example, 0.4 to 3.0 m and a thickness of 10 to 100 μm stands all over the inside of the tower. It is set up. The treated water that has flowed into the filtration tower 9 flows down by gravity from the upper end of the long fiber bundle 11 toward the lower end, and during this time, in the voids formed by the long fiber bundle 11, the water contained in the treated water is filtered. SS is captured, and the filtrate flows out from the filtrate outflow pipe 16 via the water-permeable support 12.
It enters the filtered water storage tank 19.

【0016】また、濾過塔9内に流入する固定床接触酸
化塔1の処理水中には、通常溶存酸素が存在するととも
に、固定床接触酸化塔1内の充填材3から剥離した好気
性微生物が存在するので、当該濾過塔9内においても生
物処理がなされ、有機物の更なる除去が期待できる。な
お、上記濾過塔9においては、通水初期に下降流の水流
により長繊維束11の下方部がやや屈曲してその高さが
若干縮みはするが、長繊維束11は全体的に濾過塔9内
で直立しており、流入した固定床接触酸化塔1の処理水
は直立する長繊維束11の上端から下端に向かって重力
によって通過する。
Furthermore, the treated water of the fixed bed catalytic oxidation tower 1 that flows into the filtration tower 9 usually contains dissolved oxygen, and aerobic microorganisms separated from the packing material 3 in the fixed bed catalytic oxidation tower 1 are present. Since organic substances are present, biological treatment is performed in the filter tower 9 as well, and further removal of organic substances can be expected. In the filtration tower 9, the lower part of the long fiber bundle 11 is slightly bent due to the downward water flow at the initial stage of water flow, and its height is slightly reduced. The treated water from the fixed-bed catalytic oxidation tower 1 that has flowed therethrough passes by gravity from the upper end to the lower end of the upright long fiber bundle 11.

【0017】また、通水の続行により濾過塔9の圧力損
失が増加すると、当該圧力損失の増加に伴い下方部にお
ける長繊維束11の屈曲の度合が増加するが、長繊維束
11の上端部まで屈曲する現象が生ずることはなく、通
水が終了する時点においても長繊維束11の先端はほぼ
垂直状となっている。
Furthermore, when the pressure loss in the filtration tower 9 increases due to continued water flow, the degree of bending of the long fiber bundle 11 at the lower part increases with the increase in pressure loss, but the degree of bending of the long fiber bundle 11 at the upper end of the long fiber bundle 11 increases. The phenomenon of bending does not occur until the end of the water flow, and the tips of the long fiber bundles 11 remain substantially vertical even at the end of water passage.

【0018】上述のような長繊維束11を用いた重力式
の濾過塔9は、砂利やアンスラサイト等の粒状濾材を用
いる従来の濾過塔に比較して著しく流動抵抗が少なく、
したがって重力式濾過であっても濾過速度(線速度;L
V)を20〜50m/Hと高くすることができ、そのた
め装置を小型化することができる。因に砂利やアンスラ
サイト等の粒状濾材を用いる従来の濾過塔における濾過
速度はせいぜいLV5〜10m/Hである。
The gravity-type filtration tower 9 using the long fiber bundle 11 as described above has significantly less flow resistance than the conventional filtration tower using granular filter media such as gravel or anthracite.
Therefore, even in gravity filtration, the filtration rate (linear velocity; L
V) can be made as high as 20 to 50 m/H, and therefore the device can be made smaller. Incidentally, the filtration speed in conventional filtration towers using granular filter media such as gravel and anthracite is at most LV5 to 10 m/H.

【0019】上述のような処理を続行するうちに、固定
床接触酸化塔1が目詰まり状態を呈したり、あるいは濾
過塔9の差圧が予め定めた値まで上昇した場合は、処理
を中断して以下に述べるような洗浄工程に移行する。
While continuing the above-mentioned treatment, if the fixed bed catalytic oxidation tower 1 becomes clogged or the differential pressure in the filtration tower 9 rises to a predetermined value, the treatment is interrupted. Then proceed to the cleaning process as described below.

【0020】まず、固定床接触酸化塔1の洗浄を行う場
合は、供給ポンプ8を停止して被処理水の通水を中断す
るとともに被処理水流入管7に付設した弁20および接
続管10に付設した弁21を閉とし、更に当該酸化塔1
の上部に接続した洗浄排水管14に付設した弁22を開
とする。
First, when cleaning the fixed bed catalytic oxidation tower 1, the supply pump 8 is stopped to interrupt the flow of water to be treated, and the valve 20 attached to the water inflow pipe 7 and the connecting pipe 10 are closed. The attached valve 21 is closed, and the oxidation tower 1 is further closed.
The valve 22 attached to the washing drain pipe 14 connected to the upper part of the pipe is opened.

【0021】次いで、前記被処理水流入管7に分岐接続
した洗浄用水管24を介して水用ディストリビュータ6
から洗浄水を、あるいは当該洗浄水と同時に空気流入管
5を介して空気用ディストリビュータ4から洗浄用空気
を当該接触酸化塔1内に上昇流で流入し、充填材3の表
面に着生している余剰の好気性微生物を剥離するととも
に、剥離した好気性微生物等のSSを多量に含む洗浄排
水を洗浄排水管14から排出する。
Next, the water distributor 6 is connected via the cleaning water pipe 24 branched to the water inflow pipe 7 to be treated.
The cleaning water flows upwardly into the contact oxidation tower 1 through the air inflow pipe 5, or the cleaning air flows upward from the air distributor 4 through the air inflow pipe 5, and the cleaning air is deposited on the surface of the filler 3. Excess aerobic microorganisms are removed, and cleaning waste water containing a large amount of SS such as the removed aerobic microorganisms is discharged from the washing drain pipe 14.

【0022】また、長繊維束11を充填した濾過塔9を
洗浄する場合は、当該濾過塔9の上部に接続した洗浄排
水管15に付設した弁23を開とするとともに空気流入
管18から当該濾過塔9内に圧縮空気を流入する。当該
圧縮空気の流入により、濾過塔9内の水が攪拌されると
ともに長繊維束11が振動し、繊維間で形成されていた
空隙が破壊されてSSの集合物が破壊され、また長繊維
束11に付着していたSSが剥離される。
Furthermore, when cleaning the filter tower 9 filled with the long fiber bundles 11, the valve 23 attached to the cleaning drain pipe 15 connected to the upper part of the filter tower 9 is opened, and the air inlet pipe 18 is drained from the air inflow pipe 18. Compressed air flows into the filter tower 9. Due to the inflow of the compressed air, the water in the filter tower 9 is stirred and the long fiber bundles 11 are vibrated, the voids formed between the fibers are destroyed, the SS aggregates are destroyed, and the long fiber bundles are The SS attached to 11 is peeled off.

【0023】このような圧縮空気の流入を続行したまま
、あるいは圧縮空気の流入を止め、洗浄用水管17を介
して濾過塔9内にその下部より洗浄水を流入する。当該
濾過塔9においては、前述のごとく長繊維束11の下端
が固定されているとともにその上端が自由端となってい
るので、上記洗浄水の上昇流により長繊維束11は吹き
流しのようになって伸長するとともに各繊維が振動し、
そのため長繊維束11内にSSが留まることができずに
離脱し、SSを多量に含む洗浄排水が洗浄排水管15か
ら流出する。
[0023] While continuing the inflow of compressed air as described above, or with the inflow of compressed air stopped, washing water is introduced into the filter tower 9 from the lower part thereof through the washing water pipe 17. In the filtering tower 9, the lower end of the long fiber bundle 11 is fixed as described above, and the upper end is free, so that the long fiber bundle 11 becomes like a windsock due to the upward flow of the washing water. Each fiber vibrates as it stretches.
Therefore, the SS cannot remain in the long fiber bundle 11 and separates, and washing waste water containing a large amount of SS flows out from the washing drain pipe 15.

【0024】なお、図1には塔上部が完全に開放されて
いる型の固定床接触酸化塔あるいは濾過塔を示したが、
本発明にいう「大気開放型」とは必ずしもこのような構
造のものだけを意味するものではなく、要するに塔上部
が大気と連通状態にあり、生物処理を大気圧下で、ある
いは濾過処理を重力式に行える構造であればいかなる構
造であってもよい。
Although FIG. 1 shows a fixed bed catalytic oxidation tower or filtration tower in which the upper part of the tower is completely open,
The "atmospheric open type" used in the present invention does not necessarily mean only those with such a structure; in other words, the upper part of the tower is in communication with the atmosphere, and biological treatment is performed under atmospheric pressure or filtration treatment is performed under gravity. Any structure may be used as long as it can be performed according to the formula.

【0025】[0025]

【効果】以上説明したごとく、本発明によれば固定床接
触酸化塔から流出するSSを含む処理水を、塔内に単繊
維の集合体からなる長繊維束を立設させて充填した、流
動抵抗の極めて小さい濾過塔を用いて濾過するので、重
力式濾過ではあってもLV=20〜50m/Hというよ
うな高流速での濾過が可能であり、その結果固定床接触
酸化塔の処理水中に含まれているSSを除去するための
濁質分離装置として沈殿分離槽や、砂、アンスラサイト
等の粒状濾材を充填した濾過塔を用いる従来の生物処理
装置に較べて装置全体を小型化することができるととも
に、高流速で濾過を行った場合でもSS含有量の少ない
極めて清澄な濾過水を得ることができる。
[Effects] As explained above, according to the present invention, treated water containing SS flowing out from a fixed bed catalytic oxidation tower is filled with long fiber bundles made of aggregates of single fibers standing up in the tower. Since filtration is performed using a filtration tower with extremely low resistance, it is possible to perform filtration at a high flow rate such as LV = 20 to 50 m/H even with gravity filtration.As a result, the treated water of the fixed bed catalytic oxidation tower The entire device is smaller compared to conventional biological treatment equipment that uses a sedimentation separation tank and a filtration tower filled with granular filter media such as sand and anthracite as a turbidity separation device to remove SS contained in water. In addition, extremely clear filtered water with a low SS content can be obtained even when filtration is performed at a high flow rate.

【0026】また、本発明は固定床接触酸化塔および濾
過塔を大気圧下で運転する構成としたので、両塔を加圧
下で運転する場合に較べて使用する被処理水の供給ポン
プの吐出圧が低くて済み、よって設備費が安価であると
ともに動力費も安く、また運転管理も極めて容易である
という利点を有する。
Furthermore, since the present invention has a configuration in which the fixed bed catalytic oxidation tower and the filtration tower are operated under atmospheric pressure, the discharge rate of the water supply pump used is lower than when both towers are operated under pressure. It has the advantage that the pressure is low, the equipment cost is low, the power cost is low, and operation management is extremely easy.

【0027】[0027]

【実施例】以下に本発明の実施例を説明する。直径30
cm、高さ2.0mの開放型塔内に充填材として合成樹
脂製の中空筒状ネット(商品名、ネトロンパイプ)を層
高約1.1mとなるように充填した固定床接触酸化塔と
、直径10cm、高さ2.0mの開放型塔内に、太さ3
5μ、長さ1.5mの単繊維の集合体からなる長繊維束
を75Kg/m2 の充填率となるように充填した重力
式の濾過塔とを備えた図1に示したようなフローの生物
処理装置を用い、水道水中に肉エキスペプトンをBOD
が約120mg/lとなるように溶解した被処理水の処
理を行った。
[Examples] Examples of the present invention will be described below. Diameter 30
A fixed-bed catalytic oxidation tower in which a synthetic resin hollow cylindrical net (trade name, Netron Pipe) was filled as a packing material in an open tower with a height of 2.0 m and a bed height of approximately 1.1 m. , in an open tower with a diameter of 10 cm and a height of 2.0 m, with a thickness of 3
A flow biological system as shown in Figure 1 is equipped with a gravity-type filtration tower filled with long fiber bundles consisting of aggregates of single fibers with a diameter of 5μ and a length of 1.5m at a packing rate of 75Kg/m2. BOD meat extract peptone in tap water using processing equipment
The water to be treated was treated in such a way that the amount of dissolved water was approximately 120 mg/l.

【0028】すなわち、当該被処理水を筒状ネットの表
面に予め好気性微生物を着生させた固定床接触酸化塔に
約160l/Hの流速で供給して生物処理し、次いで当
該酸化塔の処理水を前記濾過塔に供給して濾過処理を行
った。なおこの時のBOD負荷は6.0Kg/m3 ・
日、濾過速度はLV=20m/Hであった。
That is, the water to be treated is biologically treated by being supplied at a flow rate of about 160 l/H to a fixed bed catalytic oxidation tower in which aerobic microorganisms have been preliminarily grown on the surface of a cylindrical net, and then the water is biologically treated in the oxidation tower. The treated water was supplied to the filtration tower and subjected to filtration treatment. The BOD load at this time is 6.0Kg/m3.
On day one, the filtration rate was LV=20 m/H.

【0029】また、上述のような処理を続行するうちに
固定床接触酸化塔あるいは濾過塔が目詰まり状態を呈し
た場合には適宜これらの塔の洗浄を行った。定常状態に
おける平均的処理結果を表1に示す。
Further, if the fixed bed catalytic oxidation tower or the filtration tower became clogged while the above-mentioned treatment was continued, these towers were cleaned as appropriate. Table 1 shows the average processing results in steady state.

【0030】[0030]

【表1】[Table 1]

【0031】表1からわかるように、濾過塔における濾
過速度がLV=20m/Hというような高流速であるに
もかかわらず、濾過塔出口からはBOD平均10mg/
l、SS5〜8mg/lというような極めて清浄な濾過
水が得られた。
As can be seen from Table 1, even though the filtration rate in the filtration tower is as high as LV=20 m/H, an average BOD of 10 mg/H flows from the filtration tower outlet.
Very clean filtered water with SS of 5 to 8 mg/l was obtained.

【0032】[0032]

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

【図1】本発明の実施態様の一例を示すフロー説明図で
ある。
FIG. 1 is a flow explanatory diagram showing an example of an embodiment of the present invention.

【0033】[0033]

【符号の説明】[Explanation of symbols]

1…固定床接触酸化塔、2…支持床、3…充填材、4…
空気用ディストリビュータ、5…空気流入管、6…水用
ディストリビュータ、7…被処理水流入管、8…供給ポ
ンプ、9…濾過塔、10…接続管、11…長繊維束、1
2…支持床、13…被処理水貯槽、14,15…洗浄排
水管、16…濾過水流出管、17…洗浄用水管、18…
空気流入管、19…濾過水貯槽、20〜23…弁、24
…洗浄用水管
DESCRIPTION OF SYMBOLS 1... Fixed bed catalytic oxidation tower, 2... Supported bed, 3... Filler, 4...
Air distributor, 5... Air inflow pipe, 6... Water distributor, 7... Water inflow pipe, 8... Supply pump, 9... Filtration tower, 10... Connection pipe, 11... Long fiber bundle, 1
2...Supporting bed, 13...Water storage tank to be treated, 14, 15...Washing drain pipe, 16...Filtered water outflow pipe, 17...Washing water pipe, 18...
Air inflow pipe, 19... Filtered water storage tank, 20-23... Valve, 24
…Cleaning water pipe

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】好気性微生物を着生させるための充填材層
を有する大気開放型の固定床接触酸化塔の下方部に、供
給ポンプを有する被処理水流入管の一端を連通し、また
当該固定床接触酸化塔の上方部に接続管の一端を連通す
るとともに当該接続管の他端を塔内全体に長繊維束を立
設した大気開放型の濾過塔の上方部に連通し、更に当該
濾過塔の下方部に濾過水流出管の一端を連通してなり、
有機物を含む被処理水を前記供給ポンプによって固定床
接触酸化塔内に上昇流で流して大気圧下で生物処理する
とともに、生物処理を受けた固定床接触酸化塔の処理水
を、接続管を介して水位差によって前記濾過塔の上方部
に導入し、当該処理水を濾過塔内に下降流で流して重力
式に濾過する構成としたことを特徴とする生物処理装置
Claim 1: One end of a water inlet pipe having a supply pump is connected to the lower part of an air-open fixed bed catalytic oxidation tower having a packing material layer for attaching aerobic microorganisms; One end of the connecting pipe is connected to the upper part of the bed contact oxidation tower, and the other end of the connecting pipe is connected to the upper part of an air-open type filtration tower in which long fiber bundles are installed vertically throughout the tower. One end of the filtrate outflow pipe is connected to the lower part of the tower,
The water to be treated containing organic matter is flowed upward into the fixed bed catalytic oxidation tower by the supply pump and subjected to biological treatment under atmospheric pressure. A biological treatment device characterized in that the treated water is introduced into the upper part of the filtration tower by a water level difference through the filtration tower, and the treated water is caused to flow downward into the filtration tower and filtered by gravity.
JP3011527A 1991-01-08 1991-01-08 Biological treating device Pending JPH04250900A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3011527A JPH04250900A (en) 1991-01-08 1991-01-08 Biological treating device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3011527A JPH04250900A (en) 1991-01-08 1991-01-08 Biological treating device

Publications (1)

Publication Number Publication Date
JPH04250900A true JPH04250900A (en) 1992-09-07

Family

ID=11780440

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3011527A Pending JPH04250900A (en) 1991-01-08 1991-01-08 Biological treating device

Country Status (1)

Country Link
JP (1) JPH04250900A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007098242A (en) * 2005-10-03 2007-04-19 Japan Organo Co Ltd Method and apparatus for treating waste water biologically
CN103520965A (en) * 2013-10-08 2014-01-22 常州大学 Automatic device for purifying microparticle suspension in waste water

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007098242A (en) * 2005-10-03 2007-04-19 Japan Organo Co Ltd Method and apparatus for treating waste water biologically
CN103520965A (en) * 2013-10-08 2014-01-22 常州大学 Automatic device for purifying microparticle suspension in waste water

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