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JPH0126759B2 - - Google Patents
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JPH0126759B2 - - Google Patents

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Publication number
JPH0126759B2
JPH0126759B2 JP54154435A JP15443579A JPH0126759B2 JP H0126759 B2 JPH0126759 B2 JP H0126759B2 JP 54154435 A JP54154435 A JP 54154435A JP 15443579 A JP15443579 A JP 15443579A JP H0126759 B2 JPH0126759 B2 JP H0126759B2
Authority
JP
Japan
Prior art keywords
water
treated
chamber
flow rate
flow
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
JP54154435A
Other languages
Japanese (ja)
Other versions
JPS5678683A (en
Inventor
Ichiro Gonomaru
Junichi Morya
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
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 filed Critical Organo Corp
Priority to JP15443579A priority Critical patent/JPS5678683A/en
Publication of JPS5678683A publication Critical patent/JPS5678683A/en
Publication of JPH0126759B2 publication Critical patent/JPH0126759B2/ja
Granted 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)

Description

【発明の詳細な説明】 本発明は、好気性微生物をその表面に着生させ
た充填材を充填し、当該充填材層の下部あるいは
上部からBOD成分を含む被処理水を流入すると
ともに、当該充填材層の下部から空気を流入させ
て、微生物処理によつてBOD成分を除去する方
法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention involves filling a filler with aerobic microorganisms on its surface, flowing water to be treated containing BOD components from the bottom or top of the filler layer, and The present invention relates to a method for removing BOD components through microbial treatment by introducing air from the bottom of the filler layer.

従来のBOD成分の除去方法においては、固定
床接触酸化槽内に単一の充填材層を形成し、この
ような固定床接触酸化槽の充填材層の下部あるい
は上部から被処理水を流入するとともに、充填材
層の下部から空気を流入させてBOD成分の除去
を行ない、その流出水を沈殿装置あるいは浮上分
離装置などの固液分離装置に導入し、流出水中に
含まれる、充填材から剥離した汚泥などの固形物
を分離して清澄な処理水を得るが、、このときに
充填材層に目詰まりが起こると、被処理水または
処理水と、空気を充填材層の下部から、通水時よ
り大きい流量の上昇流で流入させて、充填材層の
洗浄を行なうことになり、この洗浄時に洗浄排水
が通水時の処理流量より大きい流量で多量に発生
する。当該洗浄排水を処理するについて、当該固
定床接触酸化槽のBOD成分除去の際の流出水を
処理する固液分離装置に洗浄排水をそのまま流入
させると、水量負荷が急激に増大して処理不能と
なるので、別途に、洗浄排水処理のための沈殿装
置などの固液分離装置を設置しなければならず、
その設備費が増大するという欠点がある。また洗
浄排水処理のために固液分離装置を別途に設けた
としても、当該接触酸化槽の洗浄中はBOD成分
除去の際の流出水を処理するための固液分離装置
の方が運転の中断を余儀なくされ、固液分離とい
う操作のうえで、やはり好ましいものではない。
In the conventional method for removing BOD components, a single packing material layer is formed in a fixed bed catalytic oxidation tank, and the water to be treated is introduced from the bottom or top of the packing material layer in such a fixed bed catalytic oxidation tank. At the same time, air is introduced from the bottom of the filler layer to remove BOD components, and the effluent water is introduced into a solid-liquid separation device such as a sedimentation device or flotation device to separate it from the filler material contained in the effluent water. Clear treated water is obtained by separating solids such as sludge, but if the filler layer becomes clogged, the treated water or treated water and air must be passed through from the bottom of the filler layer. The filling material layer is washed by flowing upwardly at a flow rate higher than that during water flow, and a large amount of cleaning waste water is generated during this washing at a flow rate higher than the processing flow rate during water flow. Regarding the treatment of the washing wastewater, if the washing wastewater is allowed to directly flow into the solid-liquid separator that processes the water effluent from the fixed bed contact oxidation tank during BOD component removal, the water volume load will rapidly increase and treatment will become impossible. Therefore, it is necessary to separately install a solid-liquid separation device such as a sedimentation device to treat washing wastewater.
The disadvantage is that the equipment cost increases. Furthermore, even if a solid-liquid separator is installed separately to treat washing wastewater, it is better to use a solid-liquid separator to treat runoff water during BOD component removal while the contact oxidation tank is being cleaned. This is still not desirable in terms of solid-liquid separation operations.

さらに洗浄排水と流出水とを同じ固液分離装置
を用いて処理しようとするならば、固液分離装置
の水量負荷を一定にするために、固液分離装置の
前段に大容量の中間貯槽を設けなければならない
という欠点が生ずる。
Furthermore, if cleaning wastewater and runoff water are to be treated using the same solid-liquid separator, a large-capacity intermediate storage tank should be installed before the solid-liquid separator in order to keep the water load on the solid-liquid separator constant. A disadvantage arises in that it must be provided.

本発明は、このような従来のBOD成分の除去
方法における欠点を解決するものであり、固定床
接触酸化槽を複数の室に分割することによつて、
洗浄をそれぞれの室ごとに分けて行ない、当該槽
から排出される合計の流出水と、ひとつの室にお
ける洗浄排水の流量をほぼ等しくすることによつ
て、従来から必要とされていた洗浄排水の処理を
行なう固液分離装置や、流量を一定にする洗浄排
水の中間貯槽などを省略して設備費を減少させる
ことを目的とする。
The present invention solves the drawbacks of the conventional BOD component removal method by dividing the fixed bed catalytic oxidation tank into multiple chambers.
By performing washing separately for each chamber and making the total flow rate of water discharged from the tank approximately equal to the flow rate of washing wastewater in one room, the amount of washing wastewater that was previously required can be reduced. The purpose is to reduce equipment costs by omitting solid-liquid separation equipment for processing and intermediate storage tanks for cleaning wastewater that maintain a constant flow rate.

すなわち、本発明は好気性微生物をその表面着
生させた充填材を充填し、当該充填材層の下部あ
るいは上部からBOD成分を含む被処理水を流入
するとともに、当該充填材層の下部から空気を流
入させ微生物処理によつてBOD成分を除去する
方法において、断面積がほぼ等しい複数の室に分
割した槽であつて、分割した複数の室の合計の処
理流量と、一つの室の洗浄流量とがほぼ等しくな
るように槽を分割するとともに、各室の下部ある
いは上部に被処理水供給管と各室の下部に空気供
給管をそれぞれ設けた固定床接触酸化槽を構成
し、充填材層が被処理液中に存在する固形物や余
剰微生物等で目詰まりをした時点で、各室への被
処理水の通水を停止した後、洗浄を行う一つの室
内に、被処理水の通水の際の複数の室の合計の処
理流量と等しい流量の洗浄水を空気とともに上昇
流で供給することによつて当該室内の充填材層を
洗浄し、次いでその洗浄排水を前記固定床接触酸
化槽の後段に設置した通水用の固液分離装置で処
理することによつて前記洗浄排水から固形物や余
剰微生物等を除去、すなわちBOD成分を除去す
ることを特徴とする。
That is, in the present invention, a filler having aerobic microorganisms grown on its surface is filled, water to be treated containing BOD components flows in from the bottom or top of the filler layer, and air is discharged from the bottom of the filler layer. In the method of removing BOD components through microbial treatment, the tank is divided into multiple chambers with approximately equal cross-sectional areas, and the total processing flow rate of the multiple divided chambers and the cleaning flow rate of one chamber are A fixed bed catalytic oxidation tank is constructed in which the tank is divided so that the water is almost equal to each other, and a water supply pipe to be treated is provided at the bottom or top of each chamber, and an air supply pipe is provided at the bottom of each chamber. When the water to be treated becomes clogged with solid matter, excess microorganisms, etc. present in the liquid to be treated, the flow of water to each room is stopped, and then the flow of water to one of the rooms to be cleaned is stopped. The filler layer in the chamber is washed by supplying washing water with a flow rate equal to the total treatment flow rate of the plurality of chambers together with air in an upward flow, and then the washing waste water is subjected to the fixed bed catalytic oxidation process. It is characterized in that solid matter, excess microorganisms, etc. are removed from the washing wastewater, that is, BOD components are removed by processing it with a solid-liquid separator for water flow installed at the latter stage of the tank.

以下に本発明の実施態様の一例を図面を用いて
説明する。
An example of an embodiment of the present invention will be described below with reference to the drawings.

第1図は本発明のBOD成分の除去方法を実施
する固定床接触酸化槽のフローを示した平面図で
あり、第2図は第1図のA―A′線の側断面説明
図である。これらの図中、1は好気性微生物をそ
の表面に着生させた充填材層16を有する固定床
接触酸化槽であり、当該槽1を断面積がほぼ等し
い複数の室Tたとえば、図のように三つの室T1
T2,T3に分割するとともに、当該槽の処理流量、
すなわち分割した三つの室T1,T2,T3の合計の
処理流量と、一つの室たとえばT1の洗浄流量と
がほぼ等しくなるように分割する。
FIG. 1 is a plan view showing the flow of a fixed bed catalytic oxidation tank in which the BOD component removal method of the present invention is carried out, and FIG. 2 is a side cross-sectional explanatory view taken along line A-A' in FIG. . In these figures, 1 is a fixed bed catalytic oxidation tank having a filler layer 16 with aerobic microorganisms grown on its surface. three chambers T 1 ,
In addition to dividing into T 2 and T 3 , the processing flow rate of the tank,
That is, the chambers are divided so that the total processing flow rate of the three divided chambers T 1 , T 2 , and T 3 is approximately equal to the cleaning flow rate of one chamber, for example, T 1 .

固定床接触酸化槽の全断面積は、被処理水の
BOD濃度および被処理水の流量と、あらかじめ
決定されているBOD容積負荷および充填材層高
とによつて、公知の手法によつて決定されるが、
この全断面積を有する接触酸化槽を上述した条件
に合致するように分割するのである。
The total cross-sectional area of a fixed bed contact oxidation tank is
It is determined by a known method based on the BOD concentration, the flow rate of the water to be treated, the predetermined BOD volume load and the filler layer height,
The catalytic oxidation tank having this total cross-sectional area is divided so as to meet the above-mentioned conditions.

またそれぞれの室T1,T2,T3の充填材層16
の下部に、空気供給管14を1本、あるいは複数
本を同一水平面上に均等な間隔で埋設し、また被
処理水供給管13を空気供給管14のやや上方の
水平面上に1本、あるいは複数本を均等な間隔で
同様に埋設する。また被処理水供給管13と空気
供給管14とが垂直方向に重ならないように、間
隔を置いて配設するのが望ましい。
In addition, the filling material layer 16 of each chamber T 1 , T 2 , T 3
Underneath, one or more air supply pipes 14 are buried at equal intervals on the same horizontal plane, and one or more to-be-treated water supply pipes 13 are buried on the horizontal plane slightly above the air supply pipe 14. Bury multiple pieces in the same way at equal intervals. Further, it is desirable that the treated water supply pipe 13 and the air supply pipe 14 be arranged at intervals so that they do not overlap in the vertical direction.

また被処理水切換弁3および原水ポンプ4を有
する被処理水流入管2を分岐し、それぞれの室
T1,T2,T3の被処理水供給管13に被処理水の
切換弁V1,V2,V3を介して接続し、被処理水を
それぞれの室T1,T2,T3内へ等しい流量に分配
する。また一端をブロワー5と接続させた空気流
入管6の他端を分岐し、それぞれの室T1,T2
T3の空気供給管14に空気の切換弁X1,X2,X3
を介して接続し、空気をそれぞれの室T1,T2
T3内へ等しい流量で分配する。
In addition, the treated water inflow pipe 2 having the treated water switching valve 3 and the raw water pump 4 is branched, and each chamber is
The treated water is connected to the treated water supply pipes 13 of T 1 , T 2 , and T 3 via the treated water switching valves V 1 , V 2 , and V 3 , and the treated water is transferred to the respective chambers T 1 , T 2 , and T 3 . Distribute equal flow rates into 3 . Further, one end of the air inflow pipe 6 is connected to the blower 5, and the other end is branched to form the respective chambers T 1 , T 2 ,
Air switching valves X 1 , X 2 , X 3 are installed in the air supply pipe 14 of T 3.
connect the air to each chamber T 1 , T 2 ,
Distribute equal flow into T 3 .

固定床接触酸化槽1の充填材層16の上方に流
出水の集水トレイ15を設け、当該槽1と当該槽
1の処理水と洗浄排水とを処理する共通の固液分
離装置たとえば浮上分離装置8とを流出水排出管
7で連通する。また浮上分離装置8に貯槽12を
介して処理水流出管11を接続するとともに、貯
槽12と原水ポンプ4の吸引側に洗浄水切換弁1
0を介して洗浄水管9で連通する。
A collection tray 15 for runoff water is provided above the filler layer 16 of the fixed bed contact oxidation tank 1, and a common solid-liquid separation device such as flotation separation is used to treat the tank 1 and the treated water and washing waste water of the tank 1. It communicates with the device 8 through an effluent discharge pipe 7. In addition, a treated water outflow pipe 11 is connected to the flotation separation device 8 via a storage tank 12, and a wash water switching valve 1 is connected to the storage tank 12 and the suction side of the raw water pump 4.
It communicates with the washing water pipe 9 through 0.

固定床接触酸化槽1において、被処理水を処理
する場合は、被処理水切換弁3および切換弁V1
V2,V3を開け、原水ポンプ4を起動させて、被
処理水を被処理水流入管2よりそれぞれの室T1
T2,T3に被処理水供給管13を経て、同じ流量
に分配して流入させる。たとえば原水ポンプ4を
通過する被処理水の単位時間当たりの通水流量を
Qとすると、それぞれの室T1,T2,T3に被処理
水をQ/3ずつ流入させる。これと同時に、空気
をブロワー5にて加圧し、この加圧した空気を空
気流入管6および空気の切換弁X1,X2,X3を介
して空気供給管14からそれぞれの室T1,T2
T3へ均等に分配して流入させる。
When treating water to be treated in the fixed bed contact oxidation tank 1, the water to be treated switching valve 3 and the switching valve V 1 ,
V 2 and V 3 are opened, the raw water pump 4 is started, and the water to be treated is sent from the water inflow pipe 2 to the respective chambers T 1 and
The water is distributed to T 2 and T 3 through the treated water supply pipe 13 at the same flow rate. For example, if the flow rate of the water to be treated passing through the raw water pump 4 per unit time is Q, then the water to be treated is caused to flow into each chamber T 1 , T 2 , T 3 by Q/3. At the same time, air is pressurized by the blower 5 , and the pressurized air is sent from the air supply pipe 14 to each chamber T1 , T2 ,
Evenly distribute and flow into T 3 .

このようにそれぞれの室T1,T2,T3の充填材
層16へ被処理水と空気とを上昇流で流入させ、
微生物処理によつて被処理水中のBOD成分を除
去し、その流出水を集水トレイ15を経て流出水
排出管7から浮上分離装置8へ導入する。浮上分
離装置8において、流出水中に存在する充填材か
ら剥離した汚泥などの固形分を分離し、その処理
水を小型の貯槽12を経て処理水流出管11より
流出する。
In this way, the water to be treated and air flow upward into the filling material layer 16 of each chamber T 1 , T 2 , T 3 ,
BOD components in the water to be treated are removed by microbial treatment, and the effluent is introduced into the flotation separation device 8 from the effluent discharge pipe 7 via the water collection tray 15. In the flotation separator 8, solids such as sludge exfoliated from the filler present in the outflow water are separated, and the treated water is discharged from the treated water outflow pipe 11 via a small storage tank 12.

通水をある一定時間継続し、複数の室Tの中
で、一つの室、たとえば室T1の充填材の表面に
着生した微生物が肥大化して目詰まりが起きる
と、室T1の充填材層16の洗浄を行なう。この
洗浄を行なう場合は、被処理水切換弁3を閉じ、
被処理水の室T1,T2,T3への流入を止め、、ま
た被処理水の切換弁V2,V3を閉じる。次に、洗
浄水切換弁10を開け、浮上分離装置8の処理水
を洗浄水として、貯槽12から洗浄水管9、原水
ポンプ4および切換弁V1を経て、室T1内に被処
理水供給管13から流入させる。またこれと同時
に空気の切換弁X2,X3を閉じ、ブロワー5より
発生させた加圧空気を切換弁X1を介して、室T1
内に空気供給管14から通気する。このように洗
浄水および空気を室T1内の充填材層16に上昇
流で流入させて洗浄を行ない、充填材層16から
剥離した汚泥とともに、洗浄排水を集水トレイ1
5および流出水排出管7を経て浮上分離装置8に
導入する。当該装置8において、洗浄排水に含ま
れる汚泥を分離し、処理水を得る一方、その処理
水を貯槽12および洗浄水管9を経て洗浄水とし
て循環して使用する。
If water continues to flow for a certain period of time and microorganisms that have grown on the surface of the filling material in one of the multiple chambers T, for example chamber T 1 , become enlarged and clog, the filling of chamber T 1 will be interrupted. The material layer 16 is cleaned. When performing this cleaning, close the water switching valve 3 and
Stop the flow of the water to be treated into the chambers T 1 , T 2 , T 3 , and close the switching valves V 2 , V 3 for the water to be treated. Next, the wash water switching valve 10 is opened, and the treated water from the flotation separator 8 is used as washing water to supply water to be treated from the storage tank 12 into the chamber T 1 via the wash water pipe 9, the raw water pump 4, and the switching valve V 1 . It is made to flow in from the pipe 13. At the same time, the air switching valves X 2 and X 3 are closed, and the pressurized air generated from the blower 5 is transferred to the chamber T 1 via the switching valve X 1 .
Ventilation is carried out from the air supply pipe 14 into the interior. In this way, the cleaning water and air are flowed upward into the filling material layer 16 in the chamber T 1 to perform cleaning, and the cleaning waste water along with the sludge separated from the filling material layer 16 is transferred to the water collection tray 1.
5 and the effluent discharge pipe 7 to the flotation separator 8. In the device 8, sludge contained in the washing wastewater is separated to obtain treated water, and the treated water is circulated and used as washing water via the storage tank 12 and the washing water pipe 9.

以上説明したように本発明のBOD成分の除去
方法においては、固定床接触酸化槽1は、室T1
T2,T3の合計の処理流量と、一つの室、たとえ
ば室T1の洗浄流量とがほぼ等しくなるように、
等しい断面積の室T1,T2,T3に分割してあるの
で、したがつて室T1に流入する洗浄水の流量は、
通水工程における、室T1,T2,T3の合計の処理
流量Qと等しい流量、すなわち、他の室T2,T3
への流入を止め、室T1のみに流入させるので、
通水時の約3倍の流量で洗浄水を流入させ、また
加圧空気も、他の室T2,T3への供給を止め、室
T1のみに通気するので、通水時の約3倍の流量
で通気することになり、室T1内の充填材層16
の洗浄を十分に行なうことができるとともに、当
該槽1から通水工程および洗浄工程を通じて、一
定流量の流出水あるいは洗浄排水を排出すること
ができる。
As explained above, in the BOD component removal method of the present invention, the fixed bed catalytic oxidation tank 1 has two chambers T 1 ,
so that the total processing flow rate of T 2 and T 3 and the cleaning flow rate of one chamber, for example, chamber T 1 , are approximately equal.
Since it is divided into chambers T 1 , T 2 , and T 3 with equal cross-sectional areas, the flow rate of cleaning water flowing into chamber T 1 is therefore:
In the water flow process, the flow rate is equal to the total treatment flow rate Q of chambers T 1 , T 2 , T 3 , that is, the other chambers T 2 , T 3
This will stop the flow into chamber T1 and allow it to flow only into chamber T1 .
Cleaning water flows in at a flow rate approximately three times that of water flow, and pressurized air is also stopped from being supplied to other chambers T 2 and T 3 .
Since ventilation is carried out only in chamber T 1 , the flow rate is approximately three times that when water is flowing, and the filling material layer 16 in chamber T 1 is vented.
In addition, a constant flow rate of runoff water or cleaning waste water can be discharged from the tank 1 through the water passage process and the cleaning process.

なお、室T1の洗浄を終了したのち、再び通水
工程に入り、先述の通水工程の操作と同様にし
て、それぞれの室T1,T2,T3に被処理水および
空気を供給して被処理水中のBOD成分を除去す
る。また一定時間通水を継続し、室T1,T2,T3
のうちの一つの室、たとえば室T2の充填材層1
6に目詰まりが起きると、被処理水の通水を止
め、前述の洗浄工程と同様にして、室T2のみに
洗浄水および空気を流入させて洗浄を行なう。こ
のようにして当該槽1の充填材層16の洗浄を、
それぞれの室T1,T2,T3ごとに分け、1回の洗
浄工程において一つの室Tのみの洗浄を行ない、
各洗浄工程においてそれぞれの室T1,T2,T3
洗浄を循環して行なう。
After completing the cleaning of chamber T 1 , the water flow process is started again, and the water to be treated and air are supplied to each chamber T 1 , T 2 , and T 3 in the same manner as in the water flow process described above. to remove BOD components from the water being treated. In addition, water flow continues for a certain period of time, and the chambers T1 , T2 , T3
Filler layer 1 of one of the chambers, for example chamber T 2
When clogging occurs in chamber T 6, the flow of water to be treated is stopped, and cleaning is performed by allowing cleaning water and air to flow only into chamber T 2 in the same manner as in the cleaning process described above. In this way, the filler layer 16 of the tank 1 is cleaned.
Separate the chambers T 1 , T 2 , T 3 and clean only one chamber T in one cleaning process,
In each cleaning process, the cleaning of the respective chambers T 1 , T 2 , and T 3 is performed in a circular manner.

なお本発明は実施態様で説明したようなBOD
成分を含む被処理水を充填材層の下部から流入す
る固定床接触酸化槽に限定されず、当該被処理水
を充填材層の上部から流入する固定床接触酸化槽
にも適用できることは言うまでもない。
The present invention is applicable to BOD as explained in the embodiment.
Needless to say, the present invention is not limited to a fixed bed catalytic oxidation tank in which the water to be treated containing components flows in from the bottom of the filler layer, but can also be applied to a fixed bed catalytic oxidation tank in which the water to be treated flows in from the top of the filler layer. .

本発明のBOD成分の除去方法によれば、固定
床接触酸化槽を断面積がほぼ等しい複数の室に分
割した槽であつて、分割した複数の室の合計の処
理流量と、一つの室の洗浄流量とがほぼ等しくな
るように槽を分割し、各室の下部あるいは上部に
被処理水供給管と各室の下部に空気供給管をそれ
ぞれ設け、洗浄を一つの室ごとに分けて行なうこ
とによつて、当該槽より通水工程および洗浄工程
を通して、ほぼ同じ流量の処理水および洗浄排水
が排出され、後段に設けた浮上分離装置などの固
液分離装置に連続して一定流量の処理水および洗
浄排水を流入させることができる。これによつ
て、従来のように、洗浄排水の処理を行なう固液
分離装置を別途に設ける必要もなくまた、流量を
一定にするための洗浄排水の中間貯槽を設ける必
要もなく、さらに当該槽へ流入する洗浄水の流量
が被処理水の流量とほぼ同じであるので、洗浄水
用のポンプを別途に設ける必要がなく、設備費を
減少させることができる。
According to the method for removing BOD components of the present invention, a fixed bed catalytic oxidation tank is divided into a plurality of chambers having approximately equal cross-sectional areas, and the total treatment flow rate of the plurality of divided chambers and the flow rate of one chamber are Divide the tank so that the cleaning flow rate is approximately equal, install a water supply pipe to be treated at the bottom or top of each chamber, and an air supply pipe at the bottom of each chamber, and perform cleaning separately for each chamber. As a result, almost the same flow rate of treated water and cleaning wastewater are discharged from the tank through the water flow process and the cleaning process, and a constant flow rate of treated water is continuously discharged to a solid-liquid separator such as a flotation separator installed at the subsequent stage. and cleaning wastewater can flow in. This eliminates the need to separately install a solid-liquid separator for treating washing wastewater, unlike in the past, and eliminates the need to provide an intermediate storage tank for washing wastewater to keep the flow constant. Since the flow rate of the wash water flowing into the tank is almost the same as the flow rate of the water to be treated, there is no need to separately provide a pump for the wash water, and equipment costs can be reduced.

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

第1図は本発明のBOD成分の除去方法を実施
する固定床接触酸化槽の実施態様の一例のフロー
を示した平面図であり、第2図は、第1図のA―
A′線の側断面説明図である。 1……固定床接触酸化槽、2……被処理水流入
管、3……被処理水切換弁、4……原水ポンプ、
5……ブロワー、6……空気流入管、7……流出
水排出管、8……浮上分離装置、9……洗浄水
管、10……洗浄水切換弁、11……処理水流出
管、12……貯槽、13……被処理水供給管、1
4……空気供給管、15……集水トレイ、16…
…充填材層、T……室、V……被処理水の切換
弁、X……空気の切換弁。
FIG. 1 is a plan view showing the flow of an embodiment of a fixed bed catalytic oxidation tank for carrying out the BOD component removal method of the present invention, and FIG.
FIG. 3 is a side cross-sectional explanatory view taken along line A'. 1... fixed bed contact oxidation tank, 2... treated water inflow pipe, 3... treated water switching valve, 4... raw water pump,
5...Blower, 6...Air inflow pipe, 7...Outflow water discharge pipe, 8...Flotation separation device, 9...Washing water pipe, 10...Washing water switching valve, 11...Treatment water outflow pipe, 12 ...Storage tank, 13...Water supply pipe to be treated, 1
4...Air supply pipe, 15...Water collection tray, 16...
...Filler layer, T...chamber, V...switching valve for water to be treated, X...switching valve for air.

Claims (1)

【特許請求の範囲】[Claims] 1 好気性微生物をその表面に着生させた充填材
を充填し、当該充填材層の下部あるいは上部から
BOD成分を含む被処理水を流入するとともに、
当該充填材層の下部から空気を流入させ微生物処
理によつてBOD成分を除去する方法において、
断面積がほぼ等しい複数の室に分割した槽であつ
て、分割した複数の室の合計の処理流量と、一つ
の室の洗浄流量とがほぼ等しくなるように槽を分
割するとともに、各室の下部あるいは上部に被処
理水供給管と各室の下部に空気供給管をそれぞれ
設けた固定床接触酸化槽を構成し、充填材層が被
処理液中に存在する固形物や余剰微生物等で目詰
まりをした時点で、各室への被処理水の通水を停
止した後、洗浄を行う一つの室内に、被処理水の
通水の際の複数の室の合計の処理流量と等しい流
量の洗浄水を空気とともに上昇流で供給すること
によつて当該室内の充填材層を洗浄し、次いで、
その洗浄排水を前記固定床接触酸化槽の後段に設
置した通水用の固液分離装置で処理することによ
つて前記洗浄排水から固有物や余剰微生物等を除
去することを特徴とするBOD成分の除去方法。
1. Fill with a filler with aerobic microorganisms on its surface, and then fill with a filler from the bottom or top of the filler layer.
In addition to inflowing treated water containing BOD components,
In a method in which air is introduced from the bottom of the filler layer and BOD components are removed by microbial treatment,
The tank is divided into multiple chambers with approximately equal cross-sectional areas, and the tank is divided so that the total processing flow rate of the multiple divided chambers is approximately equal to the cleaning flow rate of one chamber, and A fixed-bed contact oxidation tank is constructed with a water supply pipe to be treated at the bottom or top and an air supply pipe at the bottom of each chamber, and the filler layer is designed to prevent solid matter and excess microorganisms present in the liquid to be treated. When the blockage occurs, the flow of water to be treated to each chamber is stopped, and then a flow rate equal to the total flow rate of the multiple chambers when water is flowing is placed in one chamber to be cleaned. Cleaning the filler layer in the chamber by supplying cleaning water with air in an upward flow, and then
A BOD component characterized in that unique substances, surplus microorganisms, etc. are removed from the washing wastewater by treating the washing wastewater with a solid-liquid separator for water flow installed after the fixed bed contact oxidation tank. How to remove.
JP15443579A 1979-11-30 1979-11-30 Fixed-bed type catalytic oxidation tank Granted JPS5678683A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15443579A JPS5678683A (en) 1979-11-30 1979-11-30 Fixed-bed type catalytic oxidation tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15443579A JPS5678683A (en) 1979-11-30 1979-11-30 Fixed-bed type catalytic oxidation tank

Publications (2)

Publication Number Publication Date
JPS5678683A JPS5678683A (en) 1981-06-27
JPH0126759B2 true JPH0126759B2 (en) 1989-05-25

Family

ID=15584121

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15443579A Granted JPS5678683A (en) 1979-11-30 1979-11-30 Fixed-bed type catalytic oxidation tank

Country Status (1)

Country Link
JP (1) JPS5678683A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5547224B2 (en) * 2012-03-14 2014-07-09 株式会社東芝 Membrane filtration system

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52131647A (en) * 1976-04-27 1977-11-04 Hitachi Chem Co Ltd Contact oxidation type drainage treatment method

Also Published As

Publication number Publication date
JPS5678683A (en) 1981-06-27

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