CN107540083A - A kind of activity bacterium mud screening washer - Google Patents
A kind of activity bacterium mud screening washer Download PDFInfo
- Publication number
- CN107540083A CN107540083A CN201710894917.4A CN201710894917A CN107540083A CN 107540083 A CN107540083 A CN 107540083A CN 201710894917 A CN201710894917 A CN 201710894917A CN 107540083 A CN107540083 A CN 107540083A
- Authority
- CN
- China
- Prior art keywords
- reaction chamber
- level
- sludge
- gas plate
- screening washer
- 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.)
- Pending
Links
- 230000000694 effects Effects 0.000 title claims abstract description 22
- 241000894006 Bacteria Species 0.000 title claims abstract description 13
- 238000012216 screening Methods 0.000 title claims abstract description 13
- 239000010802 sludge Substances 0.000 claims abstract description 46
- 238000006243 chemical reaction Methods 0.000 claims abstract description 43
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 14
- 238000007599 discharging Methods 0.000 claims abstract description 5
- 238000004519 manufacturing process Methods 0.000 claims abstract description 5
- 230000001154 acute effect Effects 0.000 claims description 3
- 239000010865 sewage Substances 0.000 abstract description 13
- 238000004062 sedimentation Methods 0.000 abstract description 6
- 238000005273 aeration Methods 0.000 abstract description 4
- 238000012545 processing Methods 0.000 abstract description 3
- 239000007789 gas Substances 0.000 description 19
- 238000000034 method Methods 0.000 description 8
- 238000000926 separation method Methods 0.000 description 6
- 230000008569 process Effects 0.000 description 4
- 239000000945 filler Substances 0.000 description 3
- 230000003647 oxidation Effects 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 238000010992 reflux Methods 0.000 description 3
- 230000032683 aging Effects 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 230000036284 oxygen consumption Effects 0.000 description 2
- WFJIVOKAWHGMBH-UHFFFAOYSA-N 4-hexylbenzene-1,3-diol Chemical compound CCCCCCC1=CC=C(O)C=C1O WFJIVOKAWHGMBH-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 238000001556 precipitation Methods 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
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention discloses a kind of activity bacterium mud screening washer,Reaction chamber including box-shaped body,Bottom in the reaction chamber is provided with lambdoid swash plate base and the sludge parallel with the inclined-plane of herringbone swash plate base water inlet mud discharging mouth,The bottom surface of herringbone swash plate base and the bottom of reaction chamber are equal in magnitude,Top in reaction chamber is provided with the production mouth of a river,Both sides in the reaction chamber are sequentially provided with the one-level being obliquely installed and skim gas plate and two level slash gas plate from lower to upper,One-level exhaust outlet and secondary exhaust are additionally provided with the reaction chamber,One-level exhaust outlet is arranged on one-level and skims gas plate and reaction chamber inside outer wall junction,Secondary exhaust is arranged on two level and skims gas plate and reaction chamber inside outer wall junction,The activated sludge aeration reaction tank water outlet band mud concentration of the present invention is low,The activated sludge of discharge it is active poor,Sludge easily separates with sewage,It is few to discharge water to the activated sludge that sedimentation in secondary sedimentation tank is got off,Increase activated sludge aeration reaction tank sludge concentration,Good sewage processing effect.
Description
Technical field
The present invention relates to technical field of sewage, and in particular to a kind of activity bacterium mud screening washer.
Background technology
The conventional active sludge of biological treatment of existing sewage disposal system and biological contact oxidation process.Activated sludge process
Chi Rong great, sludge reflux is big, and sludge bulking easily occurs, and sludge flows back from second pond, because second pond main function is
Mud-water separation, hydraulic detention time length are carried out, the aerobic bacterium mud of backflow often enters simultaneous oxygen because long in the second pond residence time
Even anaerobic state, causes activated sludge strain poor activity, and after backflow, sludge self-dissolving, treatment effect is deteriorated, and has
The shortcomings of easy oxygen consumption;But activated sludge process small investment, it is simple in construction, it is easy to maintenance, turn into a kind of biological treatment generally used
Sewage method.Biological contact oxidation process, routine operation do not need sludge reflux, are less likely to occur sludge bulking, treatment effect phase
To preferable;Due to the debugging domestication operation reason before success biofilm, it is also necessary to which a large amount of sludge refluxes, biomembrane is because of sludge concentration
It is too high, easy oxygen consumption, reduce treatment effect;Increase the density of filler, investment is big, structure in design in order to increase contact surface simultaneously
Complexity, filler is more easy to aging and caking, maintenance are changed difficult;The active mycoderm of aging in contact oxidation method departs from filler and carried
Body, due to high-density packing, the technical problem such as separation difficulty.It is big sludge output to be all present in the operation of two kinds of technique, activated sludge with
Inactivated sludge is difficult to separate, and excess sludge easily causes the technical problems such as secondary pollution, poor processing effect.
So the problems such as mud-water separation, activated sludge separate with inactivated sludge, is to pass for the discharge capacity for reducing sludge
Important, mud-water separation is all using the sedimentation basin of cube point bucket, the mud-water separation effect of this sedimentation basin in existing technique
Time length bad, that sludge settling expends, is easily accessible simultaneous oxygen even anaerobic state, causes activated sludge strain poor activity;It is special
It is not that the poorer sludge settling of sludge activity is poorer, it is difficult to separate.
The content of the invention
In place of overcoming above shortcomings in the prior art, it is an object of the invention to provide a kind of activity bacterium mud
Screening washer.
The present invention is achieved through the following technical solutions:A kind of activity bacterium mud screening washer, include the reaction chamber of box-shaped body, it is described
Bottom in reaction chamber is provided with lambdoid swash plate base and the sludge parallel with the inclined-plane of herringbone swash plate base water inlet row
Mud mouth, the bottom surface of herringbone swash plate base and the bottom of reaction chamber are equal in magnitude, and the top in reaction chamber is provided with the production mouth of a river, described
Both sides in reaction chamber are sequentially provided with the one-level being obliquely installed and skim gas plate and two level slash gas plate from lower to upper, are gone back on the reaction chamber
Provided with one-level exhaust outlet and secondary exhaust, one-level exhaust outlet is arranged on one-level and skims gas plate and reaction chamber inside outer wall junction,
Secondary exhaust is arranged on two level and skims gas plate and reaction chamber inside outer wall junction.
Preferably, two-stage of the present invention skims gas plate in inside, downwardly-sloped shape and reaction chamber inside outer wall junction
Into angle.
Preferably, angle of the present invention is acute angle.
Preferably, the bottom surface of herringbone base of the present invention and the bottom of reaction chamber are equal in magnitude.
The present invention compared with prior art, has advantages below and beneficial effect:Due to living provided with above structure, the present invention
Property bacterium mud screening washer the water outlet of activated sludge aeration reaction tank band mud concentration it is low, active poor, the sludge of the activated sludge of discharge
Easily separated with sewage, it is few to discharge water to the activated sludge that sedimentation in secondary sedimentation tank is got off, and increase activated sludge aeration reaction tank sludge is dense
Degree, good sewage processing effect.
Brief description of the drawings
The detailed description made by reading with reference to the following drawings to non-limiting example, other features of the invention,
Objects and advantages will become apparent:
Fig. 1 is the structural representation of the present invention.
Embodiment
Embodiments of the invention are described below in detail, the example of the embodiment is shown in the drawings, wherein from beginning to end
Same or similar label represents same or similar element or the element with same or like function.Below with reference to attached
The embodiment of figure description is exemplary, is only used for explaining the present invention, and is not considered as limiting the invention.
In the description of the invention, it is to be understood that term " " center ", " longitudinal direction ", " transverse direction ", " on ", " under ",
The orientation or position relationship of the instruction such as "front", "rear", "left", "right", " vertical ", " level ", " top ", " bottom ", " interior ", " outer " are
Based on orientation shown in the drawings or position relationship, it is for only for ease of the description present invention and simplifies description, rather than instruction or dark
Show that the device of meaning or element there must be specific orientation, with specific azimuth configuration and operation, thus it is it is not intended that right
The limitation of the present invention.In the description of the invention, unless otherwise indicated, " multiple " are meant that two or more.
In the description of the invention, it is necessary to illustrate, unless otherwise clearly defined and limited, term " installation ", " phase
Even ", " connection " should be interpreted broadly, for example, it may be being fixedly connected or being detachably connected, or be integrally connected;Can
To be mechanical connection or electrical connection;Can also be joined directly together or be indirectly connected by intermediary, can
To be the connection of two element internals.For the ordinary skill in the art, above-mentioned term can be understood with concrete condition
Concrete meaning in the present invention.
A kind of activity bacterium mud screening washer of the present embodiment, as shown in figure 1, the reaction chamber 1 including box-shaped body, the reaction chamber
Bottom in 1 is provided with lambdoid swash plate base 2 and the sludge parallel with the inclined-plane of herringbone swash plate base 2 water inlet mud discharging mouth
3, the bottom surface and the bottom of reaction chamber 1 of herringbone swash plate base 2 are equal in magnitude, and the top in reaction chamber 1 is provided with the production mouth of a river 4, institute
State the both sides in reaction chamber 1 and be sequentially provided with the one-level slash gas plate 5 and two level slash gas plate 6 being obliquely installed from lower to upper, one-level skims gas
Plate 5 and two level skim gas plate 6 in inwardly, downwardly-sloped shape, one-level skims gas plate 5 and two level skim gas plate 6 respectively with the inner side of reaction chamber 1
It is acute angle that junction, which forms angle, and one-level exhaust outlet 7 and secondary exhaust 8, one-level exhaust outlet 7 are additionally provided with the reaction chamber 1
It is arranged on one-level and skims gas plate 5 and reaction chamber inside outer wall junction, secondary exhaust 8 is arranged on two level and skims gas plate 6 and reaction chamber 1
Inside outer wall junction.
The operation principle of the present invention:Sewage three-phase mixed liquor with aerating gas and activated sludge first is from reaction chamber 1
The sludge water inlet mud discharging mouth 3 of bottom is come in, and is then separated reacted sewage and is discharged from the production mouth of a river 4 at the top of reaction chamber 1, and gas
Body is first passed through after one-level slash gas plate 5 is skimmed and discharged from one-level exhaust outlet 7, and the gas do not discharged all again passes by two level and skims gas plate
6 skim after discharged again from secondary exhaust 8, last activated sludge and sewage it is relative without laterally disturbing in the case of, due to gravity
Effect sewage and the poor sludge of settling property with sewage up, and the preferable activated sludge of settling property down precipitation and separation
Separate out, along the inclined-plane of herringbone swash plate base 2 toward sludge water inlet mud discharging mouth 3 skid off, by the present invention can by sludge, sewage and
Three kinds of different conditions object screenings of gas.
Although an embodiment of the present invention has been shown and described, it will be understood by those skilled in the art that:Not
A variety of change, modification, replacement and modification can be carried out to these embodiments by departing under the principle and objective of the present invention, of the invention
Scope is limited by claim and its equivalent.
Claims (4)
- A kind of 1. activity bacterium mud screening washer, it is characterised in that:Reaction chamber including box-shaped body, the bottom in the reaction chamber are provided with Lambdoid swash plate base and the sludge parallel with the inclined-plane of herringbone swash plate base water inlet mud discharging mouth, herringbone swash plate base Bottom surface and reaction chamber bottom it is equal in magnitude, top in reaction chamber is provided with the production mouth of a river, and the both sides in the reaction chamber are under Up it is sequentially provided with the one-level being obliquely installed and skims gas plate and two level slash gas plate, one-level exhaust outlet and two is additionally provided with the reaction chamber Level exhaust outlet, one-level exhaust outlet are arranged on one-level and skim gas plate and reaction chamber inside outer wall junction, and secondary exhaust is arranged on two Level skims gas plate and reaction chamber inside outer wall junction.
- A kind of 2. activity bacterium mud screening washer according to claim 1, it is characterised in that:The two-stage skim gas plate in inwardly, Downwardly-sloped shape and reaction chamber inside outer wall junction are into angle.
- A kind of 3. activity bacterium mud screening washer according to claim 2, it is characterised in that:The angle is acute angle.
- A kind of 4. activity bacterium mud screening washer according to claim 1, it is characterised in that:The bottom surface of the herringbone base with The bottom of reaction chamber is equal in magnitude.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710894917.4A CN107540083A (en) | 2017-09-28 | 2017-09-28 | A kind of activity bacterium mud screening washer |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710894917.4A CN107540083A (en) | 2017-09-28 | 2017-09-28 | A kind of activity bacterium mud screening washer |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107540083A true CN107540083A (en) | 2018-01-05 |
Family
ID=60964680
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710894917.4A Pending CN107540083A (en) | 2017-09-28 | 2017-09-28 | A kind of activity bacterium mud screening washer |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107540083A (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001187394A (en) * | 1999-12-28 | 2001-07-10 | Sumitomo Heavy Ind Ltd | Waste water treatment equipment |
US20080264840A1 (en) * | 2004-06-15 | 2008-10-30 | Ecodays Co., Ltd. | Fluids Fluxion Method and Plant for Wastewater Treatment |
CN201180102Y (en) * | 2008-02-01 | 2009-01-14 | 宁波德安生态环保工程有限公司 | Biological reaction pool for wastewater treatment |
CN103395852A (en) * | 2013-08-18 | 2013-11-20 | 武汉宝捷能环境工程技术有限公司 | Inclined hole-type gas-water separator |
CN205953647U (en) * | 2016-08-24 | 2017-02-15 | 潍坊中侨环境工程有限公司 | High concentration activated sludge integrated device |
CN207498128U (en) * | 2017-09-28 | 2018-06-15 | 福建省谷神农业发展有限公司 | A kind of activity bacterium mud screening washer |
-
2017
- 2017-09-28 CN CN201710894917.4A patent/CN107540083A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2001187394A (en) * | 1999-12-28 | 2001-07-10 | Sumitomo Heavy Ind Ltd | Waste water treatment equipment |
US20080264840A1 (en) * | 2004-06-15 | 2008-10-30 | Ecodays Co., Ltd. | Fluids Fluxion Method and Plant for Wastewater Treatment |
CN201180102Y (en) * | 2008-02-01 | 2009-01-14 | 宁波德安生态环保工程有限公司 | Biological reaction pool for wastewater treatment |
CN103395852A (en) * | 2013-08-18 | 2013-11-20 | 武汉宝捷能环境工程技术有限公司 | Inclined hole-type gas-water separator |
CN205953647U (en) * | 2016-08-24 | 2017-02-15 | 潍坊中侨环境工程有限公司 | High concentration activated sludge integrated device |
CN207498128U (en) * | 2017-09-28 | 2018-06-15 | 福建省谷神农业发展有限公司 | A kind of activity bacterium mud screening washer |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103332784B (en) | Three-stage circulation aerobic reactor | |
CN104773823B (en) | A kind of A/O reactors of no pump reflux | |
CN103011402B (en) | Double-circulation anaerobic reactor | |
MX2007014364A (en) | Anaerobic purification device. | |
CN102491511B (en) | Efficient anaerobic bioreactor | |
LT5160B (en) | Method of separating suspension, in particular for waste water treatment, and an apparatus for performing the same | |
CN102471109B (en) | Reactor for anaerobically purifying waste water comprising multi-phase separator devices | |
CN105540836B (en) | Anaerobic reactor and sewage treatment process | |
CN203007035U (en) | Dual-circulation anaerobic reactor | |
CN104478080B (en) | The efficiently heavy stream aerobic reactor of honeycomb fashion | |
CN108911124A (en) | With the integral type self-supported denitrification reactor from retention anaerobic ammonium oxidizing bacteria function | |
CN202379803U (en) | Staggered flow type aeration, sediment and filter device | |
JP5064338B2 (en) | Wastewater treatment equipment | |
CN207498128U (en) | A kind of activity bacterium mud screening washer | |
KR101195006B1 (en) | Conversion of strong organic wastewater to methane through anaerobic digestion plant and process | |
CN218058594U (en) | Intensive biological method sewage treatment device | |
CN107540083A (en) | A kind of activity bacterium mud screening washer | |
CN203820591U (en) | Integrated sewage treatment equipment | |
CN207158893U (en) | Plug-flow, which declines, exposes aerobic reactor | |
CN202337712U (en) | Efficient anaerobic bioreactor | |
CN205603308U (en) | Anaerobic reactor | |
CN203360111U (en) | Three-stage circulation aerobic reactor | |
CN110818142B (en) | Treatment process of improved coagulating sedimentation dephosphorization treatment equipment | |
CN211813678U (en) | Mud-water separator | |
CN208869375U (en) | With the integral type self-supported denitrification reactor from retention anaerobic ammonium oxidizing bacteria function |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20180105 |