JPH0144395B2 - - Google Patents
Info
- Publication number
- JPH0144395B2 JPH0144395B2 JP58248809A JP24880983A JPH0144395B2 JP H0144395 B2 JPH0144395 B2 JP H0144395B2 JP 58248809 A JP58248809 A JP 58248809A JP 24880983 A JP24880983 A JP 24880983A JP H0144395 B2 JPH0144395 B2 JP H0144395B2
- Authority
- JP
- Japan
- Prior art keywords
- particles
- liquid
- tank
- wastewater
- fluidized bed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000002245 particle Substances 0.000 claims description 50
- 239000007788 liquid Substances 0.000 claims description 30
- 244000005700 microbiome Species 0.000 claims description 14
- 239000002351 wastewater Substances 0.000 claims description 14
- 238000000926 separation method Methods 0.000 claims description 11
- 238000000034 method Methods 0.000 claims description 8
- 239000000203 mixture Substances 0.000 claims description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 4
- 230000000813 microbial effect Effects 0.000 claims description 3
- 238000004062 sedimentation Methods 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 238000005299 abrasion Methods 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 1
- 239000003830 anthracite Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 239000010802 sludge Substances 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)
- Cyclones (AREA)
Description
【発明の詳細な説明】
本発明は、微生物付着粒子により構成される流
動層生物膜法の改良に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a fluidized bed biofilm process comprised of microbially attached particles.
微生物を付着させた粒子により流動層を形成さ
せ、流動層内に廃水を処理し、流動層上方で微生
物付着粒子と処理済水との分離を行なう流動層生
物膜法は公知であり、このような流動層生物膜法
においては、粒子に付着した微生物が生長し肥大
化し過ぎると粒子が処理槽から流出するので、過
剰付着の微生物を粒子から剥離しなければならな
い。この際、従来法には、以下の如き欠点があ
る。 The fluidized bed biofilm method, in which a fluidized bed is formed by particles to which microorganisms are attached, wastewater is treated in the fluidized bed, and the microorganism-adhered particles are separated from the treated water above the fluidized bed, is well known. In the fluidized bed biofilm method, if the microorganisms attached to the particles grow and become too large, the particles will flow out of the treatment tank, so the excessively attached microorganisms must be peeled off from the particles. In this case, the conventional method has the following drawbacks.
(i) 粒子をポンプ内に吸引通過させる場合には、
粒子が被損され、またポンプも摩耗される。(i) If the particles are drawn through the pump,
Particles are damaged and the pump is also worn.
(ii) 処理槽上部に撹拌機を取付け、機械的に付着
微生物を剥離する場合には、やはり粒子の破損
及び撹拌機の摩耗を生ずる。(ii) If a stirrer is attached to the top of the treatment tank and attached microorganisms are mechanically removed, particle breakage and abrasion of the stirrer will occur.
本発明はこのような従来の問題を一掃すること
を目的としてなされたもので、即ち本発明は、微
生物を付着させた粒子により処理槽内に流動層を
形成させ、流動層内で廃水を処理し、流動層上方
で微生物付着肥大粒子と処理済水との分離を行な
う廃水の流動層生物処理方法において、処理槽の
上部から微生物付着肥大粒子を含む廃水の一部を
層外付設の循環ラインを通じて取り出しながら、
該ライン上に設置した液体サイクロン内を通過さ
せることにより、上記粒子より付着微生物を剥離
させ、液体サイクロンの上部出口よりの剥離微生
物混合液は循環ラインを通じて処理槽下部に戻
し、一方下部出口よりの粒子混合液は、密閉沈降
式固液分離槽において固液分離し、分離液は液体
サイクロン上部出口よりの液に合流させ、一方沈
降粒子は、密閉型粒子溜槽に堆積させ、溜槽内に
所定量の粒子が堆積した後は、循環ポンプを通過
した後の循環液の一部を、溜槽内を通過させ、こ
れに堆積粒子を随伴しつつ処理槽下部に返送する
ことを特徴とする廃水の流動層処理法に係る。 The present invention was made with the aim of eliminating such conventional problems. Specifically, the present invention forms a fluidized bed in a treatment tank using particles to which microorganisms are attached, and treats wastewater within the fluidized bed. In a fluidized bed biological treatment method for wastewater that separates enlarged microorganism-adhered particles from treated water above the fluidized bed, a portion of the wastewater containing enlarged microorganism-adhered particles is passed from the top of the treatment tank through a circulation line installed outside the layer. While taking it out through
The adhering microorganisms are separated from the particles by passing through a liquid cyclone installed on the line, and the separated microorganism mixture from the upper outlet of the liquid cyclone is returned to the lower part of the treatment tank through the circulation line, while the liquid from the lower outlet is The particle mixture is subjected to solid-liquid separation in a closed sedimentation type solid-liquid separation tank, and the separated liquid is merged with the liquid from the upper outlet of the hydrocyclone.Meanwhile, the settled particles are deposited in a closed type particle storage tank, and a predetermined amount is stored in the tank. After the particles have accumulated, a part of the circulating liquid that has passed through the circulation pump is passed through a storage tank, and is returned to the lower part of the treatment tank while being accompanied by the accumulated particles. Concerning layer processing method.
以下図面に示すフローダイヤグラムを参照しつ
つ本発明法を詳細に説明する。 The method of the present invention will be explained in detail below with reference to the flow diagram shown in the drawings.
第1図において、廃水処理槽1には流動層ゾー
ン2及び固液分離ゾーン3が形成されている。流
動層は、予め微生物を砂、活性炭、コークス、ア
ンスラサイト、プラスチツク、ガラス、シリカゲ
ル、シリカ−アルミナ等の粒子に付着させ、馴致
させたものを浮遊させることにより、形成されて
いる。微生物付着用粒子の粒径は、その材質によ
り種々異なるが、コスト、入手の容易さ、微生物
付着の容易さ等の点で最適である砂の場合、通常
0.1〜3mm程度である。廃水処理槽1内に保持さ
るべき粒子の量は、粒子に対する微生物付着量等
により異なるが、通常槽内汚泥濃度(MLVSS)
が5000〜4000mg/程度となる様にするのが良
い。廃水は供給ライン4から循環ライン5を経て
処理槽1内に供給され、処理槽1内において、流
動層ゾーン2を上昇する間に流動層を形成してい
る微生物付着粒子にそのBOD成分及び/又は窒
素成分を与え、更にその一部は、固液分離ゾーン
3内を上昇してライン6から処理済水として系外
に取り出される。微生物の生成により肥大した微
生物付着粒子は、流動層2と固液分離ゾーン3と
の界面7の上方に浮上するので、これを循環され
る廃水の一部と一緒に循環ライン5を通じて槽外
に取り出し、槽環ライン5の途中に設置された液
体サイクロン8内を、該サイクロン8より後方設
置の循環ポンプ9の吸引作用により強制的に通過
させ、主に液体サイクロン8内で肥体粒子より付
着微生物を剥離させる。液体サイクロン8の上部
へは、剥離微生物を含有する液が上昇するので、
これを上部出口から循還ライン5を通じて処理槽
1の下部に戻し、一方液体サイクロン8の下部へ
は粒子が降下するので、これを一部の液と一緒に
下部出口より降下管10を経て、沈降式の密閉分
離槽11内に自重降下させる。分離槽11におい
ては、液は槽内を上昇するので、これをライン1
2を通じて、サイクロン8より後方の循環ライン
5に合流させ、一方粒子は槽内を降下するので、
これを降下管13を通じて、密閉型の粒子溜槽1
4内に自動降下し堆積させる。溜槽14内に所定
量の粒子が堆積した後は、降下管13に備えたバ
ルブ13aを閉じ、粒子の自動降下を停止する一
方、循環ポンプ9を通過した後の循環液の一部
を、分岐ライン15を通じて、溜槽14内を上部
から下部へ通過させ、堆積粒子をこの循環液に随
伴させて、降下管16より循環ライン5を経て処
理槽1の下部に返送させる。堆積粒子の返送を終
えた後は、分岐ライン15のバルブ15a及び降
下管16のバルブ16aを閉じ粒子返送を停止す
る一方、降下管13のバルブ13aを開き、粒子
の堆積を再開させる。このような粒子の返送操作
を繰返し行なうことにより、粒子を再生しつつ循
環使用できる。尚粒子返送操作におけるバルブ1
3a,15a及び16aの開閉切替え操作は、電
磁弁とタイマーの組合せにより周期的に行なうこ
とができる。また溜槽14内を流通される循環液
の液量増加を目的として、分岐ライン15と降下
管16の間の循環ライン5の途中に、絞り部(図
示せず)を形成することができる。 In FIG. 1, a fluidized bed zone 2 and a solid-liquid separation zone 3 are formed in a wastewater treatment tank 1. A fluidized bed is formed by adhering microorganisms to particles of sand, activated carbon, coke, anthracite, plastic, glass, silica gel, silica-alumina, etc. in advance and suspending them. The particle size of the particles for microbial adhesion varies depending on the material, but in the case of sand, which is optimal in terms of cost, ease of acquisition, ease of microbial adhesion, etc.
It is about 0.1 to 3 mm. The amount of particles that should be retained in the wastewater treatment tank 1 varies depending on the amount of microorganisms attached to the particles, but usually the sludge concentration in the tank (MLVSS)
It is best to set the amount to be about 5000 to 4000 mg/. The wastewater is supplied into the treatment tank 1 from the supply line 4 through the circulation line 5, and in the treatment tank 1, while rising through the fluidized bed zone 2, the BOD components and/or the wastewater are added to the microorganism-adhered particles forming the fluidized bed. Alternatively, a portion of the nitrogen component rises within the solid-liquid separation zone 3 and is taken out of the system as treated water through the line 6. The microorganism-adhered particles enlarged due to the production of microorganisms float above the interface 7 between the fluidized bed 2 and the solid-liquid separation zone 3, so they are transported out of the tank through the circulation line 5 together with a part of the recycled wastewater. It is taken out and forced to pass through a liquid cyclone 8 installed in the middle of the tank ring line 5 by the suction action of a circulation pump 9 installed behind the cyclone 8, and mainly adheres from the manure particles in the liquid cyclone 8. Removes microorganisms. Since the liquid containing the detached microorganisms rises to the upper part of the liquid cyclone 8,
The particles are returned to the lower part of the processing tank 1 from the upper outlet through the circulation line 5, and on the other hand, particles descend to the lower part of the hydrocyclone 8, so they are sent together with some liquid from the lower outlet through the downcomer pipe 10. It is lowered by its own weight into a sedimentation type sealed separation tank 11. In the separation tank 11, the liquid rises in the tank, so it is transferred to the line 1.
2 to join the circulation line 5 behind the cyclone 8, while the particles descend in the tank,
This is passed through a downcomer pipe 13 to a closed particle storage tank 1.
4 and deposit it automatically. After a predetermined amount of particles have accumulated in the reservoir tank 14, the valve 13a provided in the downcomer pipe 13 is closed to stop the automatic descent of the particles, while a part of the circulating fluid that has passed through the circulation pump 9 is diverted. The circulating liquid is passed through the tank 14 from the upper part to the lower part through the line 15, and the accumulated particles are returned to the lower part of the processing tank 1 via the downcomer pipe 16 and the circulation line 5. After returning the deposited particles, the valve 15a of the branch line 15 and the valve 16a of the downcomer pipe 16 are closed to stop particle return, while the valve 13a of the downcomer pipe 13 is opened to resume particle deposition. By repeatedly performing such a particle return operation, the particles can be regenerated and recycled. Valve 1 in particle return operation
Opening/closing switching operations of 3a, 15a, and 16a can be performed periodically by a combination of a solenoid valve and a timer. Further, for the purpose of increasing the amount of circulating liquid flowing through the reservoir tank 14, a constriction part (not shown) can be formed in the middle of the circulation line 5 between the branch line 15 and the downcomer pipe 16.
本発明処理法によれば、液体サイクロン8にて
再生された粒子を、循環液の一部をうまく利用し
て、循環ポンプ9を何等経由させることなしに、
処理槽1の下部に返送でき、粒子破損やポンプ磨
損などの問題を一掃できる。 According to the treatment method of the present invention, particles regenerated in the liquid cyclone 8 are effectively utilized in part of the circulating liquid, without passing through the circulation pump 9 at all.
It can be returned to the lower part of the treatment tank 1, eliminating problems such as particle damage and pump wear.
第1図は本発明の一実施態様を示すフローダイ
ヤグラム、第2図は第1図の要部拡大図である。
図に於いて、1は処理槽、2は流動層ゾーン、
3は固液分離ゾーン、4は廃水の供給ライン、5
は循環ライン、6はライン、7は界面、8は液体
サイクロン、9は循環ポンプ、10は降下管、1
1は固液分離槽、12はライン、13は降下管、
14は溜槽、15は分岐ライン、16は降下管で
ある。
FIG. 1 is a flow diagram showing one embodiment of the present invention, and FIG. 2 is an enlarged view of the main part of FIG. In the figure, 1 is a treatment tank, 2 is a fluidized bed zone,
3 is a solid-liquid separation zone, 4 is a wastewater supply line, and 5 is a solid-liquid separation zone.
is a circulation line, 6 is a line, 7 is an interface, 8 is a hydrocyclone, 9 is a circulation pump, 10 is a downcomer, 1
1 is a solid-liquid separation tank, 12 is a line, 13 is a downcomer pipe,
14 is a reservoir, 15 is a branch line, and 16 is a downcomer pipe.
Claims (1)
動層を形成させ、流動層内で廃水を処理し、流動
層上方で微生物付着肥大粒子と処理済水との分離
を行なう廃水の流動層生物処理方法において、処
理槽の上部から微生物付着肥大粒子を含む廃水の
一部を層外付設の循環ラインを通じて取り出しな
がら、該ライン上に設置した液体サイクロン内を
通過させることにより、上記粒子より付着微生物
を剥離させ、液体サイクロンの上部出口よりの剥
離微生物混合液は循環ラインを通じて処理槽下部
に戻し、一方下部出口よりの粒子混合液は、密閉
沈降式固液分離槽において固液分離し、分離液は
液体サイクロン上部出口よりの液に合流させ、一
方沈降粒子は、密閉型粒子溜槽に堆積させ、溜槽
内に所定量の粒子が堆積した後は、循環ポンプを
通過した後の循環液の一部を、溜槽内を通過さ
せ、これに堆積粒子を随伴しつつ処理槽下部に返
送することを特徴とする廃水の流動層処理法。1. Fluidized bed biological treatment of wastewater in which a fluidized bed is formed in a treatment tank using particles to which microorganisms are attached, the wastewater is treated in the fluidized bed, and the enlarged microorganism-adhered particles are separated from the treated water above the fluidized bed. In this method, a part of the wastewater containing enlarged microorganism-adhering particles is removed from the upper part of the treatment tank through a circulation line installed outside the layer, and the wastewater is passed through a liquid cyclone installed on the line, thereby removing the adhering microorganisms from the particles. The separated microbial mixture from the upper outlet of the hydrocyclone is returned to the lower part of the treatment tank through the circulation line, while the particle mixture from the lower outlet is separated into solid and liquid in a closed sedimentation type solid-liquid separation tank. The liquid from the upper outlet of the hydrocyclone is mixed with the liquid, while the settled particles are deposited in a closed particle storage tank. After a predetermined amount of particles have accumulated in the tank, a part of the circulating liquid after passing through the circulation pump is A fluidized bed treatment method for wastewater, characterized in that the wastewater is passed through a storage tank and returned to the lower part of the treatment tank while being accompanied by deposited particles.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58248809A JPS60139394A (en) | 1983-12-27 | 1983-12-27 | Biological treatment of waste water by employing fluidized bed |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58248809A JPS60139394A (en) | 1983-12-27 | 1983-12-27 | Biological treatment of waste water by employing fluidized bed |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS60139394A JPS60139394A (en) | 1985-07-24 |
JPH0144395B2 true JPH0144395B2 (en) | 1989-09-27 |
Family
ID=17183726
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP58248809A Granted JPS60139394A (en) | 1983-12-27 | 1983-12-27 | Biological treatment of waste water by employing fluidized bed |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS60139394A (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6279896A (en) * | 1985-10-03 | 1987-04-13 | Kurita Water Ind Ltd | Sewage treatment device |
JP4926349B2 (en) * | 2001-09-14 | 2012-05-09 | 住友重機械エンバイロメント株式会社 | Wastewater treatment equipment |
JP4215489B2 (en) * | 2001-11-27 | 2009-01-28 | 株式会社industria | Centrifuge |
JP5897349B2 (en) * | 2011-03-01 | 2016-03-30 | 株式会社東芝 | Solid-liquid separator |
-
1983
- 1983-12-27 JP JP58248809A patent/JPS60139394A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS60139394A (en) | 1985-07-24 |
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