JPS5930156B2 - wastewater treatment equipment - Google Patents
wastewater treatment equipmentInfo
- Publication number
- JPS5930156B2 JPS5930156B2 JP53023120A JP2312078A JPS5930156B2 JP S5930156 B2 JPS5930156 B2 JP S5930156B2 JP 53023120 A JP53023120 A JP 53023120A JP 2312078 A JP2312078 A JP 2312078A JP S5930156 B2 JPS5930156 B2 JP S5930156B2
- Authority
- JP
- Japan
- Prior art keywords
- wastewater
- small
- microorganisms
- carriers
- wastewater 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
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】
本発明は、下水など各種の廃水を処理槽に供給すると共
に、表面に廃水処理用の微生物を付着させた小担体の流
動層を処理廃水中に形成して、廃水と微生物の接触面積
を犬にし、効率良(廃水の生物化学的酸素要求量を低下
させる、あるいは同時に廃水中の有機炭素や窒素などを
除去させる廃水処理装置に関する。Detailed Description of the Invention The present invention supplies various types of wastewater such as sewage to a treatment tank, and forms a fluidized bed of small carriers with microorganisms for wastewater treatment attached to the surface in the treated wastewater. The present invention relates to a wastewater treatment system that reduces the contact area between microbes and microorganisms, reduces the biochemical oxygen demand of wastewater, and simultaneously removes organic carbon and nitrogen from wastewater.
上記の廃水処理装置によれば、単位容積当りの処理廃水
と微生物との接触面積が、単に廃水中に微生物を浮遊さ
せる場合に比して極めて大で、その処理能力を高(期待
できるものとされていたが、現実には期待したほどの高
い処理能力を得る事ができない実情にあった。According to the above-mentioned wastewater treatment equipment, the contact area between the treated wastewater and microorganisms per unit volume is extremely large compared to the case where microorganisms are simply suspended in wastewater, and the treatment capacity is high (expected). However, in reality, it was not possible to obtain the high processing power that was expected.
本発明は、そのような状況の原因を究明し、小担体の流
動層による優れた廃水の処理機能を充分に生かしきるよ
うにする事を目的とし、表面に廃水処理用微生物を付着
させた小担体の流動層を、深い下降流動部分とその下方
で接続する上昇流動部分とから形成しである処理廃水流
路のいずれにも形成すると共に、前記両流動層の夫々に
、前記小担体の取出し管により接続される付着微生物剥
離装置及び比重選別装置によって再生された小担体が、
前記各々の流動層に供給される再生装置を付設しである
事を特徴とする。The purpose of the present invention is to investigate the cause of such a situation and make full use of the excellent wastewater treatment function of the fluidized bed of small carriers. A fluidized bed of carriers is formed in both of the treated wastewater channels, which are formed by a deep downward flow section and an upward flow section connected below the deep downward flow section, and the small carriers are removed from each of the two fluidized beds. The small carriers regenerated by the attached microorganism detachment device and specific gravity sorting device connected by a pipe are
It is characterized in that a regenerator is attached to supply each of the fluidized beds.
即ち、従来装置において単位容積当りの微生物と廃水と
の接触面積増加の割には処理能力向上が不充分である事
の原因を追求したところ、微生物量の割にはその活動に
必要な溶存酸素量増加を図れない点に原因がある事を見
出したのであり、かかる着目に基いて、単に廃水流路を
深く形成するだけで、微生物の活動にとって必要な酸素
の溶存量を極めて多(し、前述の微生物を付着させた小
担体の流動層形成による優れた廃水処理機能を充分に発
揮させる事ができ、期待通りの高い処理能力でもって廃
水を短時間で浄化処理する事ができた。In other words, when we investigated the cause of the insufficient improvement in treatment capacity in the conventional equipment considering the increase in the contact area between microorganisms and wastewater per unit volume, we found that the amount of dissolved oxygen required for their activity is insufficient compared to the amount of microorganisms. They found that the cause was the inability to increase the amount of dissolved oxygen necessary for microbial activity.Based on this point of view, by simply forming deep wastewater channels, it was possible to extremely increase the amount of dissolved oxygen necessary for microbial activity. We were able to fully demonstrate the excellent wastewater treatment function by forming a fluidized bed of the small carriers to which the microorganisms were attached, and we were able to purify wastewater in a short time with the expected high treatment capacity.
殊に、前記流動層を下降及び上昇の流動部分のいずれに
も形成しであるので、上下の廃水流路を有効に利用して
処理径路並びに処理時間の短縮化を図る事ができ、装置
全体を極力小型にしながら高い処理能力を発揮させる事
ができ、しかも、前°記下降及び上昇流動部分の各々に
形成された小担体の流動層から、夫々小担体を取出して
再生した後再び供給するために、微生物と廃水との接触
面積を一定に保つことができ一定の廃水処理効率で処理
しつづけることが可能となった。In particular, since the fluidized bed is formed in both the descending and ascending fluid sections, it is possible to effectively utilize the upper and lower wastewater channels to shorten the treatment route and treatment time, and the overall system It is possible to exhibit high throughput while minimizing the size of the device, and in addition, small carriers are taken out from the fluidized bed of small carriers formed in each of the descending and upward flow sections, regenerated, and then supplied again. Therefore, the contact area between microorganisms and wastewater can be kept constant, making it possible to continue treating wastewater with a constant efficiency.
次に、本発明の実施例を図面に基づいて詳述する。Next, embodiments of the present invention will be described in detail based on the drawings.
処理すべき廃水の供給管1を備える上下に長い内筒2を
、清浄処理水取出し管3を備える上下に長い外筒4に内
装すると共に、前記内筒2の上部に、大気圧以上で過飽
和になる状態で酸素を含む気体を下向きに噴出供給する
装置5を接続して、前記廃水と気体の供給エネルギーに
よって廃水を下降させる流動部分Aを内筒2に形成する
と共に、その下降に伴う加圧によって前記気体中の酸素
を廃水中に溶解させ、かつこの溶解気体の外筒4内での
気泡化による廃水の伴流により、前記外筒4に廃水の上
昇流動部分Bを形成すると共に、廃水を下降流動部分A
にオーバーフロニによって循環供給すべ(構成し、もっ
て、下降流動部分Aと上昇流動部分Bとにわたって上下
に深い循環廃水流路を形成しである。A vertically long inner cylinder 2 equipped with a supply pipe 1 for wastewater to be treated is housed in a vertically long outer cylinder 4 equipped with a clean treated water takeout pipe 3, and a supersaturated tank 2 is installed at the upper part of the inner cylinder 2 at a pressure higher than atmospheric pressure. A device 5 for jetting and supplying oxygen-containing gas downward is connected to form a flowing portion A in the inner cylinder 2 in which the wastewater is lowered by the energy supplied from the wastewater and the gas. Oxygen in the gas is dissolved in the waste water by pressure, and the dissolved gas is bubbled in the outer cylinder 4 to create a wake of the waste water, thereby forming an upwardly flowing part B of the waste water in the outer cylinder 4, Wastewater flowing downwards part A
The wastewater is circulated and supplied by overflow, thereby forming a vertically deep circulating wastewater channel spanning the downward flow section A and the upward flow section B.
この廃水流路の下降並びに上昇の各流動部分A。Each descending and ascending flow section A of this wastewater flow path.
Bの溶存酸素濃度の高い深部に、表面に好気性廃水処理
用微生物を付着させた小担体a・・・・・・の流動層を
形成し、微生物活動のための溶存酸素量の犬なる流域に
おいて、単位容積当りの表面積の犬なる微生物と廃水と
を接触させて、廃水中の有機成分を養分として微生物を
小担体表面に付着増殖させ、廃水中の有機炭素を除去す
ると共に生物化学的酸素要求量を低下し、かつそれによ
って得られる清浄水を取出し管3から排出すべ(構成し
である。A fluidized bed of small carriers A with microorganisms for aerobic wastewater treatment attached to the surface is formed in the deep part of B where the dissolved oxygen concentration is high, creating a watershed with a large amount of dissolved oxygen for microbial activity. In this process, wastewater is brought into contact with microorganisms with a surface area per unit volume, and the microorganisms adhere to and proliferate on the surface of a small carrier using organic components in the wastewater as nutrients, removing organic carbon from the wastewater and producing biochemical oxygen. The amount of water required is reduced and the resulting clean water is discharged from the outlet pipe 3.
前記下降流動部分Aにおける小担体a・・・・・・の流
動層は、その表面に微生物を付着させた見掛は比重が廃
水よりも小なる小担体a・・・・・・を下降流動部分A
に供給して、廃水処理に伴う微生物層の増大によって、
下向き流に対する受圧面の増大による下降作用が順次大
になる事により、小担体a・・・・・・が順次下降すべ
く形成してあり、上昇流動部分Bにおける小担体a・・
・・・・の流動層は、逆に見掛は比重の犬なる小担体a
・・・・・・を上昇流動部分Bに供給して、上向き流に
対する受圧面の増大による上昇作用力が、微生物増殖に
よる重量増大の下降作用力よりも順次大になる事により
、小担体a・・・・・・が順次上昇すべ(形成しである
。The fluidized bed of the small carriers a in the downward flow section A is a downward flow of the small carriers a, which have microorganisms attached to their surfaces and whose apparent specific gravity is smaller than that of the wastewater. Part A
The increase in the microbial layer that accompanies wastewater treatment causes
As the descending action due to the increase in the pressure-receiving surface against the downward flow gradually increases, the small carriers a... are formed to descend one after another, and the small carriers a... in the upward flow portion B.
On the contrary, the fluidized bed of ... appears to be a small carrier a with a specific gravity.
... is supplied to the upward flow section B, and the upward force due to the increase in the pressure-receiving surface against the upward flow becomes larger than the downward force due to the increase in weight due to microbial growth, whereby the small carrier a ... should rise (form) sequentially.
この廃水処理において、前記小担体a・・・・・・の付
着微生物層が厚くなると、単位容積当りの微生物と廃水
乞の接触面積が減少して処理効率が低下する事となるが
、これを解消すべく小担体再生装置6.7を設けである
。In this wastewater treatment, if the layer of microorganisms attached to the small carrier a becomes thick, the contact area between the microorganisms and the wastewater per unit volume will decrease, and the treatment efficiency will decrease. In order to solve this problem, a small carrier regenerating device 6.7 is provided.
この内の下降流動部分Aの流動層の小担体a・・・・・
・に対する再生装置6は、付着微生物層が厚(なって処
理効率の低下がみられる限界線よりも流路下手側に、微
生物層の厚(なった小担体a/の取出し管8を接続する
と共に、小担体a/、・・・・・が前記限界線を越えた
事を検出する光電管リレーなどの検出機構9を内筒2に
設け、そして前記小担体取出し流路に、前記検出機構9
の検出結果に基づいて作動するポンプ・Pと、取出した
小担体a′・・・・・・の付着微生物層を剥離する装置
10、およびその表面に廃水処理用微生物を付着してい
る小担体a・・・・・・と剥離微生物とを選別する比重
選別装置11を接続する。Small carrier a in the fluidized bed in the descending flow part A...
The regenerating device 6 connects the take-out pipe 8 for the small carriers a/ with the thick microbial layer to the downstream side of the flow path below the limit line where the adhered microbial layer becomes thick and the treatment efficiency decreases. At the same time, a detection mechanism 9 such as a phototube relay for detecting that the small carriers a/, . . . exceeds the limit line is provided in the inner cylinder 2, and the detection mechanism 9
a pump P that operates based on the detection result of , a device 10 for peeling off the adhering microorganism layer of the taken out small carriers a', and the small carriers having wastewater treatment microorganisms attached to their surfaces. A specific gravity sorting device 11 for sorting out a... and detached microorganisms is connected.
尚、この比重選別装置11では、付着微生物が剥離され
た小担体a・・・・・・は見掛は比重が廃水より小であ
るために、粒径に無関係に廃水4面上に浮上分離すると
共に、剥離した微生物は沈澱し、夫夫比重選別される。In addition, in this specific gravity sorting device 11, the small carriers a from which the attached microorganisms have been peeled off appear to have a smaller specific gravity than the wastewater, so they are floated and separated on the wastewater 4 surface regardless of the particle size. At the same time, the detached microorganisms are precipitated and subjected to gravity selection.
そして、比重選別装置11で分離された再生小指体a・
・・・・・は下降流動部分Aに供給するように構成しで
ある。Then, the regenerated little finger body a.
. . . is configured to be supplied to the downward flow section A.
他方の上昇流動部分Bの小担体再生装置7は、処理効率
の低下がみられる限界線よりも流路下手側に微生物層の
厚くなった小担体a′・・−・・・の取出し管12を接
続すると共に、小担体a′・・・・・・が前記限界線を
越えた事を検出する機構13を外筒4に設け、そして前
記小担体取出し流路に、検出機構13の検出結果に基づ
いて作動するポンプP1 と付着微生物剥離装置14
、および小担体a・・・・・・と微生物とを選別分離す
る比重選別装置15を接続して、その再生小担体a・・
・・・・を上昇流動部分Bに供給すべ(構成しである。The small carrier regenerating device 7 in the other upward flow section B has a take-out pipe 12 for small carriers a', which have a thick microbial layer on the downstream side of the flow path from the limit line where the processing efficiency decreases. At the same time, a mechanism 13 for detecting that the small carrier a'... has exceeded the limit line is provided in the outer cylinder 4, and the detection result of the detection mechanism 13 is connected to the small carrier take-out flow path. Pump P1 and attached microorganism removal device 14 that operate based on
, and a specific gravity sorting device 15 for sorting and separating small carriers a... and microorganisms, and the regenerated small carriers a...
... should be supplied to the upward flow section B.
そして、前記比重選別装置j5ゼは、微生物や廃水より
見掛は比重の犬なる小担体と、剥離した微生物とを比重
選別する。Then, the specific gravity sorting device j5se separates the detached microorganisms from the small carriers which have an apparent specific gravity compared to the microorganisms and waste water.
尚、図中16は、前記比重選別装置15からの処理水を
、剥離減生物と清浄水とに分離する装置で、この装置1
6と前記比重選別装置11からの分離微生物は焼却など
の処理装置17に供給され、かつ清浄水は取出し管3に
供給される。In addition, 16 in the figure is a device that separates the treated water from the specific gravity sorting device 15 into exfoliated and reduced organisms and clean water, and this device 1
The separated microorganisms from 6 and the specific gravity sorting device 11 are supplied to a treatment device 17 such as incineration, and clean water is supplied to the take-out pipe 3.
また18は、小担体流動層の流路上手側に設けたディス
トリビュータ−で、廃水を均一流動させるべく設けられ
ている。Further, 18 is a distributor provided on the upper side of the flow path of the small carrier fluidized bed, and is provided to uniformly flow the waste water.
19・・・・・・は小担体流動層を囲う状態で張設され
た磁性体ネットで、流動層からの小担体の逃げ出しを阻
止する状態で廃水の循環流動速度を高(設定できるよう
に設けられている。19... is a magnetic net stretched to surround the small carrier fluidized bed, and the wastewater circulation flow rate can be set to high while preventing the small carriers from escaping from the fluidized bed. It is provided.
尚、酸素気体供給装置を、上昇流動部分Bの小担体流動
層の流路上手側にのみ設けると共に、下降流動部分Aに
流動層を形成するための小担体a・・・・・・に嫌気性
廃水処理用微生物を付着させれば、廃水中の窒素分の除
去を同時に行なう事ができる。The oxygen gas supply device is provided only on the upstream side of the small carrier fluidized bed in the upwardly flowing section B, and the small carriers a for forming the fluidized bed in the downwardly flowing section A are supplied with anaerobic gas. If a microorganism for treating wastewater is attached, nitrogen content in the wastewater can be removed at the same time.
図面は本発明に係る廃水処理装置の実施例を示すフロー
シートである。
a・・・・・・小担体、A・・・・・・下降流動部分、
B・・・・・・上昇流動部分。The drawing is a flow sheet showing an embodiment of the wastewater treatment apparatus according to the present invention. a...Small carrier, A...Downward flow part,
B.......Upward flow part.
Claims (1)
・・・・の流動層を、深い下降流動部分Aとその下方で
接続する上昇流動部分Bとから形成しである処理廃水流
路のいずれにも形成すると共に、前記両流動層の夫々に
、前記小担体a・・・・・・の取出し管8.12により
接続される付着微生物剥離装置10.14及び比重選別
装置11.15によって再生された小担体a・・・・・
・が、前記各々の流動層に供給される再生装置6,7を
付設しである廃水処理装置。1 Small carrier a with wastewater treatment microorganisms attached to its surface...
A fluidized bed of... is formed in both of the treated wastewater channels, which are formed from a deep downward flow section A and an upward flow section B connected below it, and in each of the two fluidized beds, The small carriers a are regenerated by the attached microorganism removal device 10.14 and the specific gravity sorting device 11.15, which are connected by the take-out pipe 8.12 of the small carriers a.
- A wastewater treatment apparatus which is equipped with regenerators 6 and 7 which are supplied to each of the fluidized beds.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53023120A JPS5930156B2 (en) | 1978-02-28 | 1978-02-28 | wastewater treatment equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53023120A JPS5930156B2 (en) | 1978-02-28 | 1978-02-28 | wastewater treatment equipment |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54115550A JPS54115550A (en) | 1979-09-08 |
| JPS5930156B2 true JPS5930156B2 (en) | 1984-07-25 |
Family
ID=12101630
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53023120A Expired JPS5930156B2 (en) | 1978-02-28 | 1978-02-28 | wastewater treatment equipment |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5930156B2 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6050547A (en) * | 1983-08-30 | 1985-03-20 | Mita Ind Co Ltd | Copying paper guide mechanism of copying machine |
| JPS6150176A (en) * | 1984-08-18 | 1986-03-12 | Matsushita Electric Ind Co Ltd | Fusing device |
| JPS62144977A (en) * | 1985-12-19 | 1987-06-29 | Seiko Epson Corp | Inkjet recording device |
| JPH02126160U (en) * | 1989-03-28 | 1990-10-17 |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4613434A (en) * | 1983-01-18 | 1986-09-23 | Oy Tampella Ab | Device for treatment of wastewater by means of anaerobic fermentation |
| CN105461059B (en) * | 2015-12-24 | 2018-03-13 | 武汉钢铁有限公司 | Integral waste water biological treatment reactor |
-
1978
- 1978-02-28 JP JP53023120A patent/JPS5930156B2/en not_active Expired
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6050547A (en) * | 1983-08-30 | 1985-03-20 | Mita Ind Co Ltd | Copying paper guide mechanism of copying machine |
| JPS6150176A (en) * | 1984-08-18 | 1986-03-12 | Matsushita Electric Ind Co Ltd | Fusing device |
| JPS62144977A (en) * | 1985-12-19 | 1987-06-29 | Seiko Epson Corp | Inkjet recording device |
| JPH02126160U (en) * | 1989-03-28 | 1990-10-17 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54115550A (en) | 1979-09-08 |
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