JPH0131354Y2 - - Google Patents
Info
- Publication number
- JPH0131354Y2 JPH0131354Y2 JP1984175162U JP17516284U JPH0131354Y2 JP H0131354 Y2 JPH0131354 Y2 JP H0131354Y2 JP 1984175162 U JP1984175162 U JP 1984175162U JP 17516284 U JP17516284 U JP 17516284U JP H0131354 Y2 JPH0131354 Y2 JP H0131354Y2
- Authority
- JP
- Japan
- Prior art keywords
- section
- wastewater
- side walls
- treatment
- partition walls
- 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
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
【考案の詳細な説明】
〔産業上の利用分野〕
本考案は廃水を担体に着成させた活性汚泥で処
理するためのコンパクトな処理装置に関し、増設
の場合、パラレルまたはシリーズに継ぎ足しので
きるユニツト型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 compact treatment device for treating wastewater with activated sludge deposited on a carrier. This invention relates to a fluidized carrier biological treatment device.
従来活性汚泥により廃水を処理する方法が広く
行われているが、その処理方法および装置におい
て種々の提案があり、BOD容積負荷を大きくせ
んとする試みも多い。活性炭、コークス、炭酸カ
ルシウム等の粉粒体を担体として、これに活性汚
泥を着成させて廃水処理の効率化を図ることも多
く行われている。
Conventionally, methods of treating wastewater using activated sludge have been widely used, but various proposals have been made regarding the treatment methods and equipment, and many attempts have been made to increase the BOD volumetric load. Activated sludge is often deposited on powdered materials such as activated carbon, coke, and calcium carbonate as carriers in order to improve the efficiency of wastewater treatment.
しかし担体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、装置の面でも効率的で
なければならない。すなわち一般的な円筒型タン
ク式装置ではスペースの割には処理量が小さく、
かつ大量の廃水を処理するためには容量にも限度
があり、その上増設は容易ではない。
However, even if wastewater can be efficiently treated by depositing activated sludge on a carrier, the equipment must also be efficient. In other words, a typical cylindrical tank-type device has a small throughput compared to its space;
In addition, there is a limit to the capacity in order to treat a large amount of wastewater, and furthermore, it is not easy to expand the capacity.
本考案者らはかかる観点から、鋭意検討した結
果、円筒型タンク式処理槽をやめ、上面長方形ま
たは正方形の角筒型槽で、かつテーパー状側壁を
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パラレルまたはシリーズ
に継ぎ足せば大量の廃水も処理することができる
コンパクトなユニツト型処理装置を考案した。す
なわち本考案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ユ
ニツト型流動担体生物処理装置において、該処理
装置は担体及び廃水を循環させる処理槽と該処理
槽の相対する両がわのオーバーフローがわに設け
た汚泥と担体の分離のための沈降分離部からな
り、該処理槽はその上部横断面が長方形または正
方形をなし、該方形の両がわのオーバーフローが
わ側壁と直角をなす2つの対辺である側壁は垂直
に立下り、該オーバーフローがわ側壁の下部は両
方とも傾斜している形状をなし、該処理槽の中央
に分割可能なエアリフト部を形成し得る2つの隔
壁を有し、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した側壁が50゜
以上の角度を有するテーパー状をなし、該各沈降
分離部は2枚以上の小隔壁を適宜間隔で配置した
ことを特徴とするユニツト型流動担体生物処理装
置である。
From this point of view, the inventors of the present invention have conducted intensive studies, and found that by eliminating the cylindrical tank-type treatment tank and adopting a rectangular cylindrical tank with a rectangular or square top and tapered side walls, an extremely efficient and efficient treatment method has been developed. We have devised a compact unit-type treatment device that can treat large amounts of wastewater even if the amount of wastewater increases by connecting them in parallel or in series. That is, the present invention provides a unit-type fluidized carrier biological treatment device in which activated sludge deposited on carrier particles is circulated around an internal partition wall while blowing air and brought into contact with inflowing wastewater. The treatment equipment consists of a treatment tank for circulating carriers and wastewater, and a sedimentation separation section for separating the sludge and carriers, which are installed on both opposing sides of the treatment tank overflow, and the treatment tank has an upper cross section. has a rectangular or square shape, the two opposite side walls that are perpendicular to the overflow side walls on both sides of the rectangle fall vertically, and the lower portions of the overflow side walls are both sloped. None, the processing tank has two partition walls capable of forming a divisible air lift section in the center, and the inclined side wall forms an angle of 50° or more for the carriers floating through the air lift section to circulate and settle. This is a unit-type fluidized carrier biological treatment device, which has a tapered shape and is characterized in that each sedimentation separation section has two or more small partition walls arranged at appropriate intervals.
本考案の装置の一実施例を図によつて説明す
る。
An embodiment of the device of the present invention will be described with reference to the drawings.
第1図は上部横断面が長方形をなす例で、Aは
その平面図であり、両側のオーバーフローがわ側
壁21,22と直角をなす2つの対辺が長辺である
側壁は垂直に立下り、オーバーフローがわ側壁2
1,22の下部31,32は両方とも傾斜している形
状をなしている。これは第1図Bに明らかであ
る。すなわち処理槽1の下部より廃水Wが流入
し、これが空気Aにより処理槽の中央の隔壁41,
42によつて形成されるエアリフトとなつて活性
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循環液の流れにつ
れて処理槽内を下降し下部に到つて再びエアリフ
トとなり、繰返し循環処理されて清浄化する。担
体粒子も循環液と共に循環するが、処理槽の両が
わの側壁21,22の下部31,32は50゜以上の角度
を有するテーパー状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。 Figure 1 shows an example in which the upper cross section is rectangular, and A is its plan view.The side walls, whose long sides are perpendicular to the overflow side walls 2 1 and 2 2 on both sides, stand vertically. Downward, overflow side wall 2
The lower portions 3 1 and 3 2 of 1 and 2 2 both have an inclined shape. This is evident in Figure 1B. That is, wastewater W flows in from the lower part of the treatment tank 1, and the air A flows through the partition wall 4 1 in the center of the treatment tank.
4 becomes an air lift formed by 2 , and floats while coming into contact with the carrier particles on which activated sludge is deposited. After floating, as shown by the arrow in the figure, the circulating fluid moves downward through the processing tank until it reaches the bottom, where it becomes an air lift again, where it is repeatedly circulated and cleaned. The carrier particles also circulate together with the circulating liquid, but because the lower portions 3 1 , 3 2 of the side walls 2 1 , 2 2 on both sides of the processing tank are tapered at an angle of 50° or more, they do not accumulate on the side walls. It is circulated to 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.
隔壁41,42を設ける位置は処理槽のほぼ中央
であるが、両隔壁の間隔は廃水量、空気量、廃水
のBOD負荷、BOD濃度、滞留時間等によつて一
定ではないので、両隔壁の間隔をB、両側壁の間
をLとすると1/2L≧B>0を満足するように適
宜選択される。 The location of the partition walls 4 1 and 4 2 is approximately in the center of the treatment tank, but the distance between the two partition walls is not constant depending on the amount of waste water, air amount, BOD load of waste water, BOD concentration, residence time, etc. Letting B be the interval between the partition walls and L be the distance between both side walls, they are appropriately selected so as to satisfy 1/2L≧B>0.
この隔壁41,42によつて形成されるエアリフ
ト部は第1図Aのように処理槽の幅を1セクシヨ
ンとするもの、第2図のように例えば3セクシヨ
ンに分割したエアリフトとするものでもよい。分
割した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
ト効果は大きい。 The air lift section formed by the partition walls 4 1 and 4 2 is such that the width of the processing tank is one section as shown in FIG. 1A, or the air lift section is divided into three sections as shown in FIG. 2. But that's fine. If the amount of air is the same when divided, the air lift effect is greater because the air does not diffuse and rises in a concentrated manner within a narrow section.
次に本考案の特徴である小隔壁51,52′,…
…及び52,52′……について説明する。 Next, the small partition walls 5 1 , 5 2 ′,...
...and 5 2 , 5 2 '... will be explained.
処理済みの廃水は、テーパーのある両側壁にあ
る小隔壁51,51′,……及び52,52′,……の
下部の空隙を経て処理水溜め61,62′に到りオ
ーバーフローして系外に排出されるが、この際オ
ーバーフロー21,22の手前に設けた沈降分離部
で担体と担体より剥離した汚泥との分離が行われ
る。すなわち担体の沈降速度は担体粒径、空孔
率、付着汚泥の見掛比重及び量によつて左右され
るが、一般に5〜15cm/分であるので、担体が系
外に流失せず、汚泥のみを処理済み廃水と共に流
出させるためには小隔壁51,52及びオーバーフ
ロー部21,22の間が処理槽内の曝気による乱流
の影響を受けることがなく、かつこの部分におけ
る水の上昇速度が上記沈降速度より小にしなけれ
ばならない。これを実現させる手段として最も簡
単には小隔壁51,52とオーバフロー部21,22
の間隔を上記乱流及び上昇速度の関係を満足する
ようにすればよいが、実際問題として小隔壁51,
52を1枚のみ設けた場合には、曝気による乱流
の影響を受けるので、この影響を避けるために小
隔壁51,52の下部と側壁31,32との間隙を小
にする必要があるが、この間隙を余り小さくする
と水の上昇速度が早くなり、かつ曝気による乱流
の効果により担体が処理水溜め61,62内に浮遊
し沈降分離ができなくなる。またこの間隙を大に
すれば小隔壁51,52による乱流の防止効果は減
少し担体の流失が起きる、これらの現象を防止す
る方法として小隔壁51,52及びオーバーフロー
部21,22の間隙を充分な大きさにする方法があ
るが、これはかなり広い間隔を必要とするので、
たとえ実施できたとしても装置の経済上不利であ
る。 The treated wastewater passes through the gaps at the bottom of the small partitions 5 1 , 5 1 ′, . . . and 5 2 , 5 2 ′ , . Eventually, the sludge overflows and is discharged outside the system, but at this time, the carrier and the sludge separated from the carrier are separated in a settling section provided before the overflows 2 1 and 2 2 . In other words, the settling speed of the carrier depends on the carrier particle size, porosity, apparent specific gravity and amount of adhered sludge, but it is generally 5 to 15 cm/min, so the carrier does not flow out of the system and the sludge In order to allow only the treated wastewater to flow out together with the treated wastewater, the area between the small partition walls 5 1 , 5 2 and the overflow parts 2 1 , 2 2 must not be affected by turbulent flow due to aeration in the treatment tank, and the water in this area must be The rate of rise must be smaller than the rate of sedimentation. The simplest means for realizing this are the small partition walls 5 1 , 5 2 and the overflow parts 2 1 , 2 2 .
The distance between the small partition walls 5 1 ,
If only one 5 2 is provided, it will be affected by turbulent flow due to aeration, so to avoid this effect, the gap between the lower part of the small partition walls 5 1 and 5 2 and the side walls 3 1 and 3 2 should be made small. However, if this gap is made too small, the rising speed of the water will increase, and the carrier will float in the treated water reservoirs 6 1 and 6 2 due to the effect of turbulent flow due to aeration, making sedimentation separation impossible. In addition, if this gap is made larger, the effect of preventing turbulent flow by the small partition walls 5 1 and 5 2 will be reduced, and the carrier will be washed away.As a way to prevent these phenomena, the small partition walls 5 1 and 5 2 and the overflow part 2 1 , 2 There is a way to make the gap between 2 large enough, but this requires a fairly wide gap, so
Even if it could be implemented, it would be economically disadvantageous for the equipment.
そこでこれらの因難は小隔壁51,52をそれぞ
れ2枚設けることにより解決できる。この場合曝
気による乱流は1枚目の小隔壁51,52によりか
なり減衰し、さらに2枚目の小隔壁51′,52′を
設けることにより担体の沈降分離が可能になる。
なお2枚の小隔壁51,51及び52,52′でも乱流
の影響が大きく沈降分離が不充分な場合は、さら
に1枚または数枚の小隔壁51″,……及び52″…
…を設ければ小隔壁とオーバーフロー部の間隔を
小に保ち得、担体の沈降分離が効率的に実施でき
る。 Therefore, these problems can be solved by providing two small partition walls 5 1 and 5 2 each. In this case, the turbulent flow caused by aeration is considerably attenuated by the first small partition walls 5 1 and 5 2 , and by providing the second small partition walls 5 1 ′ and 5 2 ′, sedimentation and separation of the carrier becomes possible.
In addition, if the effect of turbulence is large and sedimentation separation is insufficient even with the two small partition walls 5 1 , 5 1 and 5 2 , 5 2 ′, one or more small partition walls 5 1 ″, . . . and 5 2 ″…
By providing ..., the distance between the small partition wall and the overflow part can be kept small, and the sedimentation and separation of the carrier can be carried out efficiently.
循環する担体粒子は処理槽の容積の約10%を仕
込む。また吹込む空気量は処理すべき廃水の
BODと担体粒子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。 The circulating carrier particles fill approximately 10% of the volume of the treatment tank. Also, the amount of air blown is determined by the amount of air that is blown into the wastewater to be treated.
Select and determine the larger of the BOD and the amount required to flow the carrier particles by airlift.
一方処理すべき廃水の流入は処理槽の上部から
でも下部からでもよい。 On the other hand, the wastewater to be treated may flow in from the upper or lower part of the treatment tank.
本考案の処理装置は2〜60m3(例えば上面長方
形が5m×1.5m、高さ4〜5m)が最も操作し
やすく、これ以下の小容量では却つて実際の操業
上煩雑となる。また、これ以上の容量を必要とす
る場合には、このユニツト型処理装置を第3図の
ようにシリーズに3基あるいはパラレルに必要と
するユニツト数を継ぎ足して設ければ少なくとも
各ユニツト内においては空気の分配、分散が容易
に均一に実施することができ、また処理水のオー
バーフローも均一にすることができるから操作が
容易で、しかも大量の廃水を処理することができ
る。 The processing apparatus of the present invention is easiest to operate when it has a capacity of 2 to 60 m 3 (for example, a rectangular top surface of 5 m x 1.5 m and a height of 4 to 5 m), and a small capacity smaller than this becomes rather complicated in actual operation. In addition, if a larger capacity is required, at least within each unit, three units of this unit type processing equipment can be installed in series or the required number of units can be added in parallel as shown in Figure 3. Air distribution and dispersion can be easily and uniformly carried out, and overflow of treated water can also be made uniform, so operation is easy and a large amount of wastewater can be treated.
本考案の処理装置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。本装置は一定の容量にすること
によつて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、この空気量の範囲内でエ
アリフトを形成させ、かつ小隔壁の枚数と間隔を
適宜選択すれば経済的に廃水を処理できる。さら
に装置の容量が足りない場合は必要なユニツト数
を継ぎ足すことにより対処でき、この際装置の形
状が上面長方形または正方形で継ぎ足すに便なる
ためコンパクトに設置できるので、設置場所は大
きい面積を要しない利点がある。
The processing device of the present invention may be made of iron or concrete, and in particular, if it is made of concrete, the manufacturing cost will be extremely low. By setting a constant capacity, this device forms an air lift within the range of the 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, and the number and spacing of small partition walls can be adjusted. If appropriate selection is made, wastewater can be treated economically. Furthermore, if the capacity of the device is insufficient, it can be solved by adding the necessary number of units.In this case, the shape of the device is rectangular or square on the top, making it convenient to add units, so it can be installed compactly, so the installation location does not require a large area. It has the advantage of not being necessary.
第1図は本考案のユニツト型流動担体生物処理
装置の一実施例を示す図で、Aは平面図、Bは縦
断面図である。第2図はエアリフト部を分割した
実施例の平面図、第3図は本考案のユニツト型処
理装置を継ぎ足した場合の平面図である。
1……処理槽、21,22……オーバーフロー部
(側壁)、31,32……テーパー部、41,42……
隔壁、51,51′,51″,……52,52′,52″……
小隔壁、61,62……処理水溜め、7……担体粒
子、A……空気、W……廃水。
FIG. 1 is a diagram showing an embodiment of the unit type fluidized carrier biological treatment apparatus of the present invention, in which A is a plan view and B is a longitudinal sectional view. FIG. 2 is a plan view of an embodiment in which the air lift section is divided, and FIG. 3 is a plan view of a case in which a unit type processing apparatus of the present invention is added. DESCRIPTION OF SYMBOLS 1...Processing tank, 21 , 22 ...Overflow part (side wall), 31 , 32 ...Tapered part, 41,42 ...
Partition wall, 5 1 , 5 1 ′, 5 1 ″, ... 5 2 , 5 2 ′, 5 2 ″...
Small partition wall, 6 1 , 6 2 ... treated water reservoir, 7 ... carrier particles, A ... air, W ... wastewater.
Claims (1)
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ユニツト型流動担
体生物処理装置において、該処理装置は担体及び
廃水を循環させる処理槽と該処理槽の相対する両
がわのオーバーフローがわに設けた汚泥と担体の
分離のための沈降分離部からなり、該処理槽はそ
の上部横断面が長方形または正方形をなし、該方
形の両がわのオーバーフローがわ側壁と直角をな
す2つの対辺である側壁は垂直に立下り、該オー
バーフローがわ側壁の下部は両方とも傾斜してい
る形状をなし、該処理槽の中央に分割可能なエア
リフト部を形成し得る2つの隔壁を有し、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
ための前記傾斜した側壁が50゜以上の角度を有す
るテーパー状をなし、該各沈降分離部は2枚以上
の小隔壁を適宜間隔で配置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。 In a unit-type fluidized carrier biological treatment equipment, activated sludge deposited on carrier particles is circulated around an internal partition wall while blowing air, and brought into contact with inflowing wastewater for treatment. and a treatment tank for circulating wastewater, and a sedimentation separation section for separating sludge and carriers provided on opposite sides of the overflow side of the treatment tank, and the treatment tank has a rectangular or square upper cross section. The two opposite side walls that are perpendicular to the overflow side walls on both sides of the rectangle fall vertically, and the lower portions of the overflow side walls are both sloped. The tank has two partition walls capable of forming a divisible air lift section in the center thereof, and the inclined side wall has a tapered shape having an angle of 50° or more for the carriers floating through the air lift section to circulate and settle. None, a unit type fluid carrier biological treatment device, characterized in that each sedimentation separation section has two or more small partition walls arranged at appropriate intervals.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1984175162U JPH0131354Y2 (en) | 1984-11-20 | 1984-11-20 |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1984175162U JPH0131354Y2 (en) | 1984-11-20 | 1984-11-20 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6191398U JPS6191398U (en) | 1986-06-13 |
| JPH0131354Y2 true JPH0131354Y2 (en) | 1989-09-26 |
Family
ID=30732766
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1984175162U Expired JPH0131354Y2 (en) | 1984-11-20 | 1984-11-20 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0131354Y2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2588712B2 (en) * | 1987-04-10 | 1997-03-12 | 建設省建築研究所長 | Wastewater treatment equipment |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5820680B2 (en) * | 1977-06-29 | 1983-04-25 | 栗田工業株式会社 | Fluidized bed sewage treatment equipment |
| JPS57207596A (en) * | 1981-06-16 | 1982-12-20 | Ngk Insulators Ltd | Fluidized bed type waste water treating device |
| JPS5843997U (en) * | 1981-09-18 | 1983-03-24 | 株式会社神戸製鋼所 | Biological treatment equipment for wastewater |
-
1984
- 1984-11-20 JP JP1984175162U patent/JPH0131354Y2/ja not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6191398U (en) | 1986-06-13 |
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