JPH0157639B2 - - Google Patents
Info
- Publication number
- JPH0157639B2 JPH0157639B2 JP60280968A JP28096885A JPH0157639B2 JP H0157639 B2 JPH0157639 B2 JP H0157639B2 JP 60280968 A JP60280968 A JP 60280968A JP 28096885 A JP28096885 A JP 28096885A JP H0157639 B2 JPH0157639 B2 JP H0157639B2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- carrier
- wall
- unit type
- biological treatment
- 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
Links
- 239000002351 wastewater Substances 0.000 claims description 26
- 238000005192 partition Methods 0.000 claims description 22
- 239000012530 fluid Substances 0.000 claims description 17
- 238000000926 separation method Methods 0.000 claims description 11
- 239000010802 sludge Substances 0.000 claims description 11
- 239000000969 carrier Substances 0.000 claims description 8
- 238000004062 sedimentation Methods 0.000 claims description 8
- 239000002245 particle Substances 0.000 description 11
- 238000005273 aeration Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000009434 installation Methods 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 235000014653 Carica parviflora Nutrition 0.000 description 1
- 241000243321 Cnidaria Species 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
Description
【発明の詳細な説明】
〔産業上の利用分野〕
この発明は、廃水を担体に着成させた活性汚泥
で処理する流動担体生物処理装置に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a fluidized carrier biological treatment device for treating wastewater with activated sludge deposited on a carrier.
しかしながら、この珊瑚粉末に活性汚泥を着成
させて効率的に廃水を処理し得るにしても、装置
の面からみてその効率を発揮させるには充分なも
のでなく、特に廃水が増加した場合にその処理量
に限界がある。また、この種の処理装置を設置す
るには大きな面積を要するし、設置場所の大きさ
に対応させることができず問題点があつた。
However, even if it is possible to efficiently treat wastewater by depositing activated sludge on this coral powder, it is not sufficient to demonstrate its efficiency from the equipment perspective, especially when the amount of wastewater increases. There is a limit to the amount of processing. Furthermore, installing this type of processing device requires a large area, and it is difficult to adapt it to the size of the installation location, which poses a problem.
この発明の目的は、一般的な円筒型タンク式の
処理装置にあるいは大型化した処理装置に代え
て、横断面長方形状の角筒型の処理槽を採用する
ことにより、極めて効率的でしかも処理すべき廃
水が増加しても、複数個のユニツト型流動担体生
物処理装置をパラレル又はシリーズに隣接して設
置ができ、言い換えると、継ぎ足しができ、コン
パクトに構成することができる処理装置を提供す
ることである。 The purpose of this invention is to achieve extremely efficient processing by adopting a prismatic cylindrical processing tank with a rectangular cross section instead of a general cylindrical tank type processing equipment or a large processing equipment. To provide a treatment device which allows a plurality of unit type fluidized carrier biological treatment devices to be installed in parallel or adjacent to each other in series even when the amount of wastewater to be treated increases, in other words, can be supplemented and can be configured compactly. That's true.
この発明は、上記の問題点を解消し、上記の目
的を達成するために、次のように構成されてい
る。即ち、この発明は、対向状態で且つ少なくと
もいずれか一方に傾斜壁部を有する両側壁と対向
状態の平行壁部から成る両側壁とから形成した担
体及び廃水を循環させる処理槽を有し、前記処理
槽内に沈降部を形成すると共に前記処理槽のオー
バフロー側に汚泥と担体の分離のために沈降分離
部を形成し、更に前記処理槽内に取外し可能な隔
壁によつてエアリフト部を形成し、しかも前記処
理槽の前記側壁と別の前記処理槽の前記側壁とが
互いに接触状態になるように複数個の前記処理槽
を隣接して配置可能に構成したことを特徴とする
ユニツト型流動担体生物処理装置に関する。
In order to solve the above problems and achieve the above objects, the present invention is configured as follows. That is, the present invention has a treatment tank in which waste water is circulated and a carrier formed of opposite side walls having an inclined wall portion on at least one side and both side walls having parallel wall portions facing each other. A settling part is formed in the treatment tank, a settling separation part is formed on the overflow side of the treatment tank for separating sludge and carriers, and an air lift part is further formed in the treatment tank by a removable partition wall. , a unit type fluidized carrier characterized in that a plurality of the processing tanks can be arranged adjacently so that the side wall of the processing tank and the side wall of another processing tank are in contact with each other. Regarding biological treatment equipment.
また、このユニツト型流動担体生物処理装置
は、前記エアリフト部を通つて浮上する担体が循
環沈降するための前記傾斜壁部を50゜以上の角度
に傾斜させ、また前記沈降分離部を前記傾斜壁部
の上方に小隔壁を垂設して形成したものである。 Further, in this unit type fluidized carrier biological treatment apparatus, the inclined wall part for circulating and settling the carriers floating through the air lift part is inclined at an angle of 50 degrees or more, and the sedimentation separation part is connected to the inclined wall. It is formed by hanging a small partition above the section.
この発明は、上記のように構成されており、次
のように作用する。即ち、このユニツト型流動担
体生物処理装置における担体及び廃水を循環させ
る処理槽の少なくとも1つの側壁は傾斜した形状
であるので、担体粒子は循環液と共に側壁に滞留
することなく循環させることができる。また、前
記処理槽は、対向状態で且つ少なくともいずれか
一方に傾斜壁部を有する両側壁と対向状態の平行
壁部から成る両側壁とから形成し、しかも前記処
理槽の前記側壁と別の前記処理槽の前記側壁とが
互いに接触状態になるように複数個の前記処理槽
を隣接して配置可能に構成したので、廃水量に応
じて1個或いは複数の前記処理槽を設置すること
ができ、しかも設置場所の広さに応じて適宜の数
だけの前記処理槽を設置することができ、ユニツ
ト型流動担体生物処理装置自体をコンパクトに構
成し、廃水量に応じた処理能力を発揮させる。
This invention is configured as described above and operates as follows. That is, since at least one side wall of the treatment tank for circulating the carrier and waste water in this unit type fluidized carrier biological treatment apparatus has an inclined shape, the carrier particles can be circulated together with the circulating liquid without staying on the side wall. Further, the processing tank is formed of both side walls facing each other and having an inclined wall portion on at least one side, and both side walls having parallel wall portions facing each other, and further, Since the plurality of treatment tanks can be arranged adjacently so that the side walls of the treatment tanks are in contact with each other, one or more treatment tanks can be installed depending on the amount of wastewater. Furthermore, an appropriate number of treatment tanks can be installed depending on the size of the installation location, and the unit type fluid carrier biological treatment apparatus itself is compactly constructed and exhibits treatment capacity according to the amount of wastewater.
以下、図面を参照して、この発明によるユニツ
ト型流動担体生物処理装置の実施例を説明する。
第1図A及び第1図Bにおいて、この発明による
ユニツト型流動担体生物処理装置の一実施例が示
されている。第1図Aはこの発明によるユニツト
型流動担体生物処理装置の一実施例を示す平面
図、及び第1図Bは第1図Aの縦断面図である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, embodiments of a unit type fluid carrier biological treatment apparatus according to the present invention will be described with reference to the drawings.
1A and 1B, one embodiment of a unit type fluid carrier biological treatment apparatus according to the present invention is shown. FIG. 1A is a plan view showing an embodiment of a unit type fluid carrier biological treatment apparatus according to the present invention, and FIG. 1B is a longitudinal sectional view of FIG. 1A.
このユニツト型流動担体生物処理装置は、担体
粒子に着成させた活性汚泥を、空気を吹込みつつ
内部に設けた隔壁の周りを循環させて流入する廃
水と接触させて処理するものである。第1図Aに
おいて、このユニツト型流動担体生物処理装置に
おける処理槽1が長方形の形状に形成された状態
が示されている。処理槽1は担体粒子9及び廃水
を循環させる槽を形成するものであり、処理槽1
は横断面が長方形に形成され、該長方形の長辺に
相当する対向状態の側壁が平行壁部に形成され、
且つ第1図Bに示すように、長方形の短辺に相当
する2つの側壁2の一方が垂直に立下り、他方が
傾斜した傾斜壁部4に形成されている。また、垂
直に立下つた平行壁部の側壁との間に、隔壁5を
分割可能に配置し、該隔壁5によつて処理槽1内
部にエアリフト部10を形成している。第1図B
において、処理槽1の下部より廃水を矢印Wで示
すように流入させ、処理槽1の一方の立下り側壁
2と隔壁5との間に形成されたエアリフト部10
を、廃水が空気(図の矢印Aで示す)によつて活
性汚泥を着成させた担体粒子と接触しつつ浮上す
る。浮上後は図中矢印のように流れは循環し、処
理槽1内を下降し下部に到り、再びエアリフト部
10を通つて繰り返し循環処理され、清浄化す
る。担体粒子9も循環液と共に循環するが、エア
リフト部10の反対側の側壁即ち傾斜壁部4は、
50゜以上の角度を有する傾斜構造となつているの
で、側壁に滞留せずに循環させられる。角度が
50゜未満では循環液に伴われない担体粒子が一部
側壁に残り、これが嫌気状態となつて微生物の好
気性消化を妨げるので好ましくない。処理槽1の
オーバフロー部3側には、汚泥と担体9の分離の
ための沈降分離部が形成されている。この沈降分
離部は、傾斜した傾斜壁部の上方に小隔壁6を垂
設することによつて形成されている。 This unit-type fluidized carrier biological treatment apparatus treats activated sludge deposited on carrier particles by circulating it around an internal partition wall while blowing air into it and bringing it into contact with inflowing wastewater. FIG. 1A shows a state in which a treatment tank 1 in this unit type fluidized carrier biological treatment apparatus is formed into a rectangular shape. The treatment tank 1 forms a tank in which carrier particles 9 and waste water are circulated.
has a rectangular cross section, and opposite side walls corresponding to the long sides of the rectangle are formed as parallel walls,
In addition, as shown in FIG. 1B, one of the two side walls 2 corresponding to the short sides of the rectangle is vertically downward, and the other is formed as an inclined wall portion 4. Further, a partition wall 5 is disposed separably between the side wall of the vertically falling parallel wall section, and an air lift section 10 is formed inside the processing tank 1 by the partition wall 5. Figure 1B
, wastewater is caused to flow in from the lower part of the treatment tank 1 as shown by the arrow W, and the air lift section 10 formed between one of the falling side walls 2 of the treatment tank 1 and the partition 5
The wastewater floats up while coming into contact with carrier particles on which activated sludge has been deposited by air (indicated by arrow A in the figure). After floating, the flow circulates as shown by the arrow in the figure, descends in the processing tank 1, reaches the lower part, and is repeatedly circulated and cleaned through the air lift section 10 again. Although the carrier particles 9 also circulate together with the circulating fluid, the side wall opposite the air lift section 10, that is, the inclined wall section 4,
Since it has an inclined structure with an angle of 50 degrees or more, it can be circulated without stagnation on the side wall. The angle is
If the angle is less than 50°, part of the carrier particles that are not accompanied by the circulating fluid will remain on the side wall, creating an anaerobic state and hindering aerobic digestion of microorganisms, which is not preferable. A sedimentation separation section for separating sludge and carriers 9 is formed on the overflow section 3 side of the treatment tank 1 . This sedimentation/separation section is formed by suspending a small partition wall 6 above the inclined wall section.
エアリフト部10を形成する隔壁5を設ける位
置は、廃水量、空気量、廃水のBOD負荷、BOD
濃度、滞留時間等によつて一定ではないが、立下
り側壁と傾斜した傾斜壁部4の立下り部分との距
離の中央点より立下り側壁までの間で適宜選択さ
れる。即ち、立下り側壁と隔壁5との間の距離を
Bとし、両側壁の距離(槽の長さ)をLとすれば
1/2L≧B>0である。この隔壁5は、例えば、
第1図Aに示すように、処理槽1の幅を1セクシ
ヨンのエアリフト部10を形成してもよく、第3
図Bに示すように、3セクシヨンに分割したエア
リフト部10に形成してもよく、また、第4図B
に示すように、エアリフト部10を円形の数セク
シヨンのエアリフト部10に形成してもよい。処
理槽1に設けるエアリフト部10は、分割した構
造の方が空気量が同一の場合、空気が拡散せず狭
い区画内を集中して上昇するのでエアリフト効果
が大きい。循環する担体粒子9は、処理槽1の容
積の約10%を仕込む。また吹き込む空気量は処理
すべき廃水のBODと担体粒子9をエアリフトに
よつて流動させるために必要な量のいずれか大き
い方を選んで決定する。一方、処理すべき廃水の
流入は、処理槽1の上部からでも下部からでもよ
い。 The position where the partition wall 5 forming the air lift section 10 is installed is determined based on the amount of waste water, the amount of air, the BOD load of the waste water, and the BOD.
Although it is not constant depending on the concentration, residence time, etc., it is appropriately selected between the center point of the distance between the falling side wall and the falling part of the inclined wall portion 4 to the falling side wall. That is, if the distance between the falling side wall and the partition wall 5 is B, and the distance between both side walls (the length of the tank) is L, then 1/2L≧B>0. This partition wall 5 is, for example,
As shown in FIG. 1A, the width of the processing tank 1 may be one section to form an air lift section 10, and a third section may be formed.
As shown in Figure B, the air lift section 10 may be divided into three sections.
As shown in FIG. 2, the air lift portion 10 may be formed into several circular sections. The air lift section 10 provided in the processing tank 1 has a larger air lift effect in a divided structure because when the air amount is the same, the air does not diffuse and rises in a concentrated manner within a narrow section. The circulating carrier particles 9 fill approximately 10% of the volume of the processing tank 1. Further, the amount of air to be blown is determined by selecting the larger of the BOD of the wastewater to be treated and the amount required to flow the carrier particles 9 by the air lift. On the other hand, the wastewater to be treated may flow in from the upper or lower part of the treatment tank 1.
処理済みの廃水は、傾斜した側壁にある小隔壁
6の下部の空隙を経て処理水溜め8に到りオーバ
フローして系外に排出される。この際、オーバフ
ロー部3の手前に設けた沈降分離部により担体9
から剥離した汚泥と担体9とを分離する。この沈
降分離部は、担体9の沈降速度がその粒径、空孔
率、付着汚泥及びその量により左右されるが、一
般に、5〜15cm/minであるので、担体9が系外
に流失しないようにする目的に適するものであれ
ばいかなる方法でも差し支えないが、小隔壁6及
びオーバフロー部3の間が処理槽1内の曝気によ
る乱流の影響を受けることがなく、且つ上昇速度
が上記沈降速度より小になればよい。なお、図中
7は傾斜板を示す。 The treated wastewater passes through the gap at the bottom of the small partition wall 6 on the inclined side wall, reaches the treated water reservoir 8, overflows, and is discharged outside the system. At this time, the carrier 9 is
The sludge separated from the carrier 9 is separated from the carrier 9. In this sedimentation separation section, the sedimentation rate of the carrier 9 depends on its particle size, porosity, adhering sludge and its amount, but is generally 5 to 15 cm/min, so the carrier 9 does not flow out of the system. Any method may be used as long as it is suitable for the purpose of achieving the above-mentioned sedimentation. It should be smaller than the speed. Note that 7 in the figure indicates an inclined plate.
この発明の処理装置は1〜20m3(例えば、上面
長方形の長手方向長さ2m、短手方向幅1m、高
さ4〜5m)が最も操作し易く、これ以上の小容
積では却つて実際の操作上煩雑となる。そこで、
処理すべき廃水量が多量になれば、処理槽1を複
数個配置して廃水を処理することができる。例え
ば、第5図に示すように、2基の処理槽1をシリ
ーズに継ぎ足して配置することができる。即ち、
処理槽1の側壁と別の処理槽1の側壁とが、第5
図に示すように、互いに接触状態になるように2
個の処理槽1を隣接して配置する。或いは、第6
図に示すように、3基の処理槽1をパラレルに継
ぎ足して設置することもできる。即ち、処理槽1
の側壁と別の処理槽1の側壁とが、第6図に示す
ように、互いに接触状態になるように3個の処理
槽1を隣接して配置する。 The processing equipment of this invention is easiest to operate when the volume is 1 to 20 m 3 (for example, the length of the upper rectangle is 2 m in the longitudinal direction, the width in the lateral direction is 1 m, and the height is 4 to 5 m). Operation becomes complicated. Therefore,
If the amount of wastewater to be treated becomes large, a plurality of treatment tanks 1 can be arranged to treat the wastewater. For example, as shown in FIG. 5, two processing tanks 1 can be arranged in series. That is,
The side wall of the processing tank 1 and the side wall of another processing tank 1 are connected to the fifth
2 so that they are in contact with each other as shown in the figure.
The processing tanks 1 are arranged adjacent to each other. Or the sixth
As shown in the figure, three processing tanks 1 can be installed in parallel. That is, processing tank 1
The three processing tanks 1 are arranged adjacent to each other so that the side wall of one processing tank 1 and the side wall of another processing tank 1 are in contact with each other, as shown in FIG.
このユニツト型流動担体生物処理装置を、第5
図に示すように、2基継ぎ足す代わりに、第2図
A及び第2図Bに示すように、処理槽1を2基分
を立下がり側壁を省いて継ぎ足した構成に形成す
ることもできる。 This unit type fluid carrier biological treatment equipment was installed in the fifth
Instead of adding two processing tanks 1 as shown in the figure, it is also possible to form a structure in which two processing tanks 1 are added by omitting the falling side walls, as shown in Fig. 2A and Fig. 2B. .
第2図A及び第2図Bにおいて、この発明によ
るユニツト型流動担体生物処理装置の別の実施例
が示されている。第2図Aはこの発明によるユニ
ツト型流動担体生物処理装置の別の実施例を示す
平面図、及び第2図Bは第2図Aの縦断面図であ
る。このユニツト型流動担体生物処理装置は、処
理槽11が上記実施例の処理槽1と比較して、処
理槽1を2基分を立下がり側壁を省いて継ぎ足し
た形に形成した以外については全く同一の構成及
び作用を有しているので、同一の構成及び機能に
ついての説明はここでは省略する。 2A and 2B, another embodiment of a unit type fluid carrier biological treatment apparatus according to the present invention is shown. FIG. 2A is a plan view showing another embodiment of the unit type fluid carrier biological treatment apparatus according to the present invention, and FIG. 2B is a longitudinal sectional view of FIG. 2A. This unit-type fluidized carrier biological treatment apparatus has no other features than the treatment tank 11 of the above embodiment, except that the treatment tank 11 is formed in the form of two treatment tanks 1, with the falling side walls omitted and added. Since they have the same configuration and function, explanations regarding the same configuration and function will be omitted here.
このユニツト型流動担体生物処理装置の処理槽
11は、横断面が長方形に形成され、長方形の長
辺に相当する対向状態の側壁が平行な平行壁部に
形成され、且つ長方形の短辺に相当する両側壁が
傾斜した傾斜壁部4に形成されている。処理槽1
1内に分割可能なエアリフト部10を形成し得る
隔壁5,5′が設けられている。エアリフト部1
0を通つて浮上する担体9が循環沈降するため、
処理槽における側壁の傾斜壁部4は50゜以上の角
度に傾斜しており、沈降分離部は傾斜した傾斜壁
部4の上方に小隔壁6を垂設している。この処理
槽11にエアリフト部10を形成するための隔壁
5,5′の間隔B′については、処理槽1における
間隔Bの関係式1/2L≧B>0から、間隔B′は間
隔2Bであるから、1/2L≧1/2B′>0であればよ
い。この隔壁5,5′で形成されたエアリフト部
10内を右廻りと左廻りのエアリフトが形成され
る。更に、隔壁5,5′で形成されたエアリフト
部10を、第3図B又は第4図Bに示すように、
数セクシヨンに分割することも勿論可能である。 The processing tank 11 of this unit type fluidized carrier biological treatment apparatus has a rectangular cross section, and has parallel side walls facing each other corresponding to the long sides of the rectangle, and parallel walls corresponding to the short sides of the rectangle. A sloped wall portion 4 is formed with both side walls sloped. Processing tank 1
Partition walls 5, 5' are provided within which a divisible air lift section 10 can be formed. Air lift part 1
Since the carrier 9 floating through 0 circulates and settles,
The inclined wall portion 4 of the side wall of the treatment tank is inclined at an angle of 50° or more, and the sedimentation and separation section has a small partition wall 6 suspended above the inclined inclined wall portion 4. Regarding the interval B' between the partition walls 5 and 5' for forming the air lift part 10 in the processing tank 11, from the relational expression 1/2L≧B>0 for the interval B in the processing tank 1, the interval B' is the interval 2B. Therefore, it is sufficient if 1/2L≧1/2B′>0. Clockwise and counterclockwise airlifts are formed within the airlift portion 10 formed by the partition walls 5, 5'. Furthermore, as shown in FIG. 3B or FIG. 4B, the air lift portion 10 formed by the partition walls 5 and 5' is
Of course, it is also possible to divide it into several sections.
この発明によるユニツト型流動担体生物処理装
置は、上記のように構成されているので、次のよ
うな効果を有する。即ち、このユニツト型流動担
体生物処理装置は、対向状態で且つ少なくともい
ずれか一方に傾斜壁部を有する両側壁と対向状態
の平行壁部から成る両側壁とから形成した担体及
び廃水を循環させる処理槽を有し、前記処理槽内
に沈降部を形成すると共に前記処理槽のオーバフ
ロー側に汚泥と担体の分離のための沈降分離部を
形成し、更に前記処理槽内に取外し可能な隔壁に
よつてエアリフト部を形成し、しかも前記処理槽
の前記側壁と別の前記処理槽の前記側壁とが互い
に接触状態になるように複数個の前記処理槽を隣
接して配置可能に構成したので、前記処理槽を複
数個設置することによつて所要の廃水量に対応す
る容量に処理装置を構成することができ、また、
廃水の種類によつて異なる廃水の流入量及び空気
必要量に応じて空気量の範囲内で前記エアリフト
部を形成させることができ、経済的に廃水を処理
できる。
Since the unit type fluid carrier biological treatment apparatus according to the present invention is constructed as described above, it has the following effects. That is, this unit-type fluidized carrier biological treatment apparatus is a treatment system in which wastewater and a carrier are circulated, which are formed by opposite side walls having inclined walls on at least one side and opposite parallel walls. A settling section is formed in the treatment tank, a settling separation section is formed on the overflow side of the treatment tank for separating sludge and carriers, and a removable partition is provided in the treatment tank. In addition, the plurality of processing tanks can be arranged adjacently so that the side wall of the processing tank and the side wall of another processing tank are in contact with each other. By installing multiple treatment tanks, the treatment equipment can be configured to have a capacity that corresponds to the required amount of wastewater, and
The air lift portion can be formed within a range of air amount according to the inflow amount of waste water and the required amount of air, which differ depending on the type of waste water, so that waste water can be treated economically.
即ち、前記処理槽の容量が1個で足りない場合
には、パラレル又はシリーズに複数個の前記処理
槽を互いに隣接して設置すること、言い換える
と、前記処理槽を複数個継ぎ足すことにより対処
でき、この際、前記処理槽の形状が対向状態で且
つ少なくともいずれか一方に傾斜壁部を有する両
側壁と対向状態の平行壁部から成る両側壁とから
形成した形状、言い換えれば、前記処理槽の横断
面が長方形で継ぎ足すのに好ましい形状であるの
で、所定の場所に複数個の前記処理槽をコンパク
トに設置でき、設置場所の広さに応じた配置にす
ることができる利点がある。 That is, if the capacity of one treatment tank is insufficient, it can be dealt with by installing a plurality of treatment tanks adjacent to each other in parallel or in series, in other words, by adding a plurality of treatment tanks. In this case, the shape of the processing tank is formed of both side walls facing each other and having an inclined wall portion on at least one side and both side walls consisting of parallel wall portions facing each other, in other words, the processing tank Since the cross section of the tank is rectangular, which is a suitable shape for addition, there is an advantage that a plurality of the processing tanks can be compactly installed at a predetermined location and can be arranged according to the size of the installation location.
更に、前記処理槽を複数個設置した場合には、
前記処理槽内にそれぞれ独立して前記エアリフト
部が形成されるので、前記各処理槽毎に一様な散
気状態を得ることができる。それ故に、従来の1
個の処理槽内に複数のエアリフト部を設けた処理
装置では、該処理槽内で散気状態が不均一になつ
て担体が片寄り、流動層が一様でなくなるような
現象が発生していたが、この発明によるユニツト
型流動担体生物処理装置は、各処理槽毎に一様な
散気状態を得ることができるので、前記各処理槽
内に担体がそれぞれ均一に分散して最も好ましい
流動状態を確保することができる。 Furthermore, when multiple treatment tanks are installed,
Since the air lift portions are formed independently in the processing tanks, a uniform aeration state can be obtained for each processing tank. Therefore, the conventional 1
In processing equipment that has multiple air lift sections in each processing tank, phenomena such as uneven aeration conditions within the processing tank, causing the carriers to shift and the fluidized bed to become uneven, occur. However, the unit type fluidized carrier biological treatment apparatus according to the present invention can achieve a uniform aeration condition in each treatment tank, so that the carriers are uniformly dispersed in each treatment tank and the most preferable flow rate is achieved. state can be secured.
また、前記担体も循環液と共に循環するが、前
記傾斜壁部が50゜以上の角度を有する傾斜構造で
あるので、前記担体が前記処理槽の側壁に滞留せ
ずに循環させられ、循環液に伴われない担体粒子
が一部側壁に残り、該担体が嫌気状態となつて微
生物の好気性消化を妨げる現象は発生しない。更
に、前記処理槽のオーバフロー側には、傾斜した
前記傾斜壁部の上方に小隔壁を垂設することによ
つて沈降分離部が形成されているので、汚泥と前
記担体の分離が確実に達成され、前記処理槽内の
曝気による乱流の影響を受けることがなく、且つ
上昇速度が上記沈降速度より小になるように構成
できる。 Further, the carrier also circulates together with the circulating liquid, but since the inclined wall portion has an inclined structure having an angle of 50° or more, the carrier is circulated without staying on the side wall of the processing tank, and is not included in the circulating liquid. A part of the unaccompanied carrier particles remains on the side wall, and the carrier becomes anaerobic, thereby preventing the aerobic digestion of microorganisms from occurring. Further, on the overflow side of the treatment tank, a settling separation section is formed by vertically installing a small partition above the inclined wall section, so that separation of the sludge and the carrier is reliably achieved. It can be constructed such that it is not affected by turbulent flow due to aeration in the processing tank, and the rising speed is smaller than the settling speed.
また、前記処理槽は鉄製でもコンクリート製で
もよく、特にコンクリート製にすれば製作費も極
めて廉価となる。前記処理槽は、例えば、従来の
円筒型タンク式のものと比較して担体の流出量が
極めて少ないので、廃水を安定的に効率よく処理
することができる。 Further, the treatment tank may be made of iron or concrete, and in particular, if it is made of concrete, the manufacturing cost will be extremely low. Since the treatment tank has an extremely small amount of carrier flow out compared to, for example, a conventional cylindrical tank type, wastewater can be treated stably and efficiently.
第1図Aはこの発明によるユニツト型流動担体
生物処理装置の一実施例を示す平面図、第1図B
は第1図Aの縦断面図、第2図Aはこの発明によ
るユニツト型流動担体生物処理装置の別の実施例
を示す平面図、第2図Bは第2図Aの縦断面図、
第3図Aはこの発明によるユニツト型流動担体生
物処理装置の更に別の実施例を示す縦断面図、第
3図Bは第3図Aの平面図、第4図Aはこの発明
によるユニツト型流動担体生物処理装置の他の実
施例を示す縦断面図、第4図Bは第4図Aの平面
図、第5図はこの発明によるユニツト型流動担体
生物処理装置の処理槽を継ぎ足した一実施例を示
す平面図、及び第6図はこの発明によるユニツト
型流動担体生物処理装置の処理槽を継ぎ足した別
の実施例を示す平面図である。
1……処理槽、2……垂直立下がり側壁、3…
…オーバフロー部、4……傾斜壁部、5,5′…
…隔壁、6……小隔壁、8……処理水溜め、9…
…担体粒子。
FIG. 1A is a plan view showing an embodiment of a unit type fluid carrier biological treatment apparatus according to the present invention, and FIG. 1B
is a longitudinal sectional view of FIG. 1A, FIG. 2A is a plan view showing another embodiment of the unit type fluid carrier biological treatment apparatus according to the present invention, FIG. 2B is a longitudinal sectional view of FIG. 2A,
FIG. 3A is a longitudinal sectional view showing still another embodiment of the unit type fluid carrier biological treatment apparatus according to the present invention, FIG. 3B is a plan view of FIG. 3A, and FIG. 4A is a unit type fluidized carrier biological treatment apparatus according to the present invention. FIG. 4B is a plan view of FIG. 4A, and FIG. 5 is a longitudinal cross-sectional view showing another embodiment of the fluid carrier biological treatment apparatus, and FIG. FIG. 6 is a plan view showing an embodiment of the present invention, and FIG. 6 is a plan view showing another embodiment in which a treatment tank is added to the unit type fluid carrier biological treatment apparatus according to the present invention. 1... Processing tank, 2... Vertical falling side wall, 3...
...Overflow part, 4...Slanted wall part, 5, 5'...
...Partition wall, 6...Small partition wall, 8...Treated water reservoir, 9...
...Carrier particles.
Claims (1)
斜壁部を有する両側壁と対向状態の平行壁部から
成る両側壁とから形成した担体及び廃水を循環さ
せる処理槽を有し、前記処理槽内に沈降部を形成
すると共に前記処理槽のオーバフロー側に汚泥と
担体の分離のための沈降分離部を形成し、更に前
記処理槽内に取外し可能な隔壁によつてエアリフ
ト部を形成し、しかも前記処理槽の前記側壁と別
の前記処理槽の前記側壁とが互いに接触状態にな
るように複数個の前記処理槽を隣接して配置可能
に構成したことを特徴とするユニツト型流動担体
生物処理装置。 2 前記エアリフト部を通つて浮上する担体が循
環沈降するための前記傾斜壁部を50゜以上の角度
に傾斜させ、また前記沈降分離部を前記傾斜壁部
の上方に小隔壁を垂設して形成したことを特徴と
する請求項1に記載のユニツト型流動担体生物処
理装置。[Scope of Claims] 1. A treatment tank for circulating wastewater and a carrier formed of opposite side walls having an inclined wall portion on at least one side and both side walls consisting of opposite parallel wall portions, A settling part is formed in the treatment tank, a settling separation part is formed on the overflow side of the treatment tank for separating sludge and carriers, and an air lift part is further formed in the treatment tank by a removable partition wall. Further, the unit type flow system is characterized in that a plurality of the processing tanks can be arranged adjacently so that the side wall of the processing tank and the side wall of another processing tank are in contact with each other. Carrier biological treatment equipment. 2. The inclined wall part for circulating and settling the carriers floating through the air lift part is inclined at an angle of 50 degrees or more, and the sedimentation separation part is provided with a small partition wall hanging above the inclined wall part. The unit type fluid carrier biological treatment device according to claim 1, characterized in that the unit type fluid carrier biological treatment device is formed.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60280968A JPS61167499A (en) | 1985-12-16 | 1985-12-16 | Unit type biological treatment device with fluid carrier |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60280968A JPS61167499A (en) | 1985-12-16 | 1985-12-16 | Unit type biological treatment device with fluid carrier |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57056611A Division JPS58174289A (en) | 1982-04-07 | 1982-04-07 | Biologically treating device of unit type using fluidized carrier |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61167499A JPS61167499A (en) | 1986-07-29 |
| JPH0157639B2 true JPH0157639B2 (en) | 1989-12-06 |
Family
ID=17632400
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60280968A Granted JPS61167499A (en) | 1985-12-16 | 1985-12-16 | Unit type biological treatment device with fluid carrier |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61167499A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0677743B2 (en) * | 1987-04-13 | 1994-10-05 | 良一 白潟 | Unit type water treatment facility |
| JPH02214597A (en) * | 1989-02-16 | 1990-08-27 | Hitachi Plant Eng & Constr Co Ltd | Device for nitrifying sewage |
-
1985
- 1985-12-16 JP JP60280968A patent/JPS61167499A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61167499A (en) | 1986-07-29 |
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