CN205556252U - Be applied to water body remediation's intermittent type pulse aeration equipment - Google Patents

Be applied to water body remediation's intermittent type pulse aeration equipment Download PDF

Info

Publication number
CN205556252U
CN205556252U CN201620091110.8U CN201620091110U CN205556252U CN 205556252 U CN205556252 U CN 205556252U CN 201620091110 U CN201620091110 U CN 201620091110U CN 205556252 U CN205556252 U CN 205556252U
Authority
CN
China
Prior art keywords
aeration
water
control
intermittent pulse
gas outlet
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.)
Active
Application number
CN201620091110.8U
Other languages
Chinese (zh)
Inventor
徐颋
梁新强
沈超峰
李育才
周琪
俞忠力
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
ZHEJIANG METHYL SOURCE LIFE TECHNOLOGY Co.,Ltd.
Original Assignee
Zhejiang June-5 Environment Technology Co Ltd
Zhejiang Weitan Technology Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Zhejiang June-5 Environment Technology Co Ltd, Zhejiang Weitan Technology Co Ltd filed Critical Zhejiang June-5 Environment Technology Co Ltd
Priority to CN201620091110.8U priority Critical patent/CN205556252U/en
Application granted granted Critical
Publication of CN205556252U publication Critical patent/CN205556252U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)

Abstract

The utility model belongs to the water treatment field relates to a be applied to water body remediation's intermittent type pulse aeration equipment, including setting up in underwater aeration structure, the aeration structural connection is oriented the air feed structure of aeration structure air feed, the air feed structure with be provided with the control structure of control aeration structure intermittent type nature aeration between the aeration structure, the control structure include with the seal chamber of air feed structure intercommunication, seal chamber sets up the gas outlet, gas outlet department device control valve, seal chamber passes through the gas outlet with the aeration structural connection. The efficiency of the dissolved oxygen is improved, energy -conservation is realized to the energy saving, and it is muddy to reduce the water, has kept the water limpid.

Description

A kind of intermittent pulse aerator being applied to water remediation
Technical field
This utility model relates to a kind of aerator, a kind of intermittent pulse aeration dress being applied to water remediation Put, belong to water harnessing field.
Background technology
The pollution of water body (river course, lake, reservoir etc.) is day by day serious, the most around sanitary wastewater, all kinds of hotel, school Sanitary sewage and the sanitary sewage of two sides resident, the pollution of other organic sewage.Traditional regulating water environment method is main Have following several, and have following defects that
1, chemical restoration
The essence of chemical restoration is to utilize the chemistry of chemical agent complexity and materialization effect (to include neutralization, complexation, generation Gas or precipitation, demulsification, colloid unstability, extract, condense with flocculation), forward pollutant to another thing phase, pollutant from aqueous phase Although states of matter change, but the most fundamentally eliminate pollutant, and add medicament and be easily generated secondary pollution.
2, physical restoration
Physical restoration is primarily referred to as by diversion desilting, machinery except measures such as algaes, gets rid of the pollutant in water.So Although pollution of river problem can temporarily be solved, but can not fundamentally solve the pollution of river, because As time goes on, two The resident living sewage of bank and enterprise produce waste water and are continually drained, and over time, quality of river water can be reduced to pollution control Front state.Furthermore, this kind of method needs large-scale structures and plant equipment, costly.
3, bio-ecological restoration technology
Bio-ecological restoration technology refers to utilize specific biological (plant, microorganism or protozoacide) to absorb, converts, Remove or degradation water environmental contaminants, it is achieved the measure that water environment purifies, ecological effect is recovered.Repair process can naturally, in situ Ground is carried out, construction investment is only chemical method, Physical is repaired 30~50.Bio-ecological restoration technology is owing to having peace The plurality of advantages such as Quan Xing, economy, practicality, systematicness and become the technical way of apparatus for treating river water pollution.
A, water plant recovery technique.
Utilize water plant and the microenvironment of symbiosis thereof being suitable for corresponding river water body environment, remove the pollution in water body Thing.Water plant and planktonic algae are competitors on nutrient substance and in the utilization of water energy, and it can effectively suppress planktonic algae Growth.But, water plant cultivates growth rate slowly, and treatment effect is difficult to take effect in a short time.And, to some water environments Poor river course, water plant is cultivated very difficult.
B, aquatic animal recovery technique.
Aquatic animal includes zooplankton, necton and zoobenthos, and they are with the free bacteria in water body, swim alga Class, organic debris etc. are food, can effectively reduce the float in water body, improve the transparency of water body.But, the breeding of excess Can cause again the pollution of water body, simultaneously water plant repair can only be river course is carried out desilting after could realize.
C, bio membrane treatment.
Bio membrane treatment refers to that utilizing natural material (such as cobblestone), synthetic material (such as fiber) is carrier, at it Surface forms a kind of special biomembrane, and biofilm surface is long-pending big, can be that microorganism provides bigger bond area, be conducive to adding The strong Degradation to pollutant.But, complete this work, be the most also intended to river course is carried out desilting, furthermore, the pollution of river Time serious, this technical role is little.
The various defects existed based on above-mentioned existing processing mode, at present, use under water that aeration is to water reoxygenation, and effect is bright Aobvious, it is widely used, but, existing aeration mode also there is also some defects: the problem of aeration is that bed mud is stirred the most under water Dynamic, cause water body muddy;2., constantly to oxygen supply of water body, keep high dissolved oxygen, the waste energy etc..Have much room for improvement.
Utility model content
For the drawbacks described above overcoming existing aeration mode to exist, this utility model provides a kind of water remediation that is applied to Intermittent pulse aerator, improves dissolved oxygen efficiency, saves the energy, it is achieved energy-conservation, reduces water body muddy, maintains water body limpid.
In order to achieve the above object, this utility model adopts the following technical scheme that: a kind of be applied between water remediation Having a rest intermission aeration device, including the aeration structure being arranged under water, described aeration structure connects oriented described aeration structure supply Gas-supplying structure, be provided with between described gas-supplying structure and described aeration structure control aeration structure intermittence aeration control knot Structure, described control structure includes the sealing cavity connected with described gas-supplying structure, and described sealing cavity arranges gas outlet, described in go out Arranging control valve at QI KOU, described sealing cavity is connected with described aeration structure by described gas outlet.
As preferably, described gas-supplying structure is air compressor machine or blower fan.
As preferably, described aeration structure includes conveying pipe and the aeration opening being arranged on described conveying pipe, described aeration Mouth is provided with aeration board.
As preferably, described control structure sets the housing sealing cavity in including, is provided with volume regulation in described cavity Part.
As preferably, described aeration board is tapered micro holes aeration board.
As preferably, the micropore size of described tapered micro holes aeration board is 0.1-0.5mm.
As preferably, described volume regulating part is adjustment disk and controls the telescopic cylinder that described adjustment disk moves up and down, institute Stating and be provided with sealing ring on the outer ring of adjustment disk, described adjustment disk is connected with the inner wall sealing of described control structure housing.
By implementing technique scheme, this utility model has the advantage that
(1) dissolved oxygen efficiency is improved, it is achieved energy-conservation.Continuous aeration so that remain high dissolved oxygen levels in water, causes new Send into the dissolved oxygen in water to be difficult to dissolving, a kind of oxygen supply and the waste of the energy.Intermittent aerating so that in water body Dissolved oxygen concentration forms a time gradient, and i.e. when starting, dissolved oxygen levels is minimum, it is easy to dissolve the oxygen sent in water Gas, at the end of, dissolved oxygen rises to the highest, then slow consumption, more back and forth, and the most energy-conservation, peak efficiency utilizes to be sent into Oxygen.
(2) prevent continuous bed mud from stirring, reduce water body muddy.Continuous aeration can cause bed mud to be constantly stirred, and makes Water body is muddy;Intermittent aerating has one period stopping aeration, and the time can be had to allow bed mud precipitate, or bed mud and water mixing again Precipitation is formed, it is therefore prevented that muddy before forming colloid.
(3) gradient of dissolved oxygen, intermittently water disturbance, defines little ecological diversity, contributes to water body purification.Expose continuously Gas makes the continuous disturbance of water body, and keeps constant dissolved oxygen so that water body habitat keeps steady state, does not utilize bio-diversity Build;Intermittent aerating so that Dissolved Oxygen in Water forms the distribution of temporal Concentraton gradient, contributes to water aerobic bacteria, oxygen bacterium of holding concurrently Multiformity growing environment, and water body holding interval disturbance, contribute to swimming type, the growing environment of sessile form microorganism so that Microorganisms in water and other hydrobiological formation multiformity, contribute to the biological cleaning of water body.
(4) contribute to the growth of submerged vegetation, improve water body purification ability, reduce energy consumption.Intermittent aerating, reduces bed mud and stirs Dynamic, reduce muddiness, contribute to submerged vegetation growth, submerged vegetation itself possesses efficient water body purification ability, and also can carry Oxygen in water supply, it is possible to reduce energy consumption needed for aeration.
Accompanying drawing explanation
Accompanying drawing 1 is the schematic diagram of this utility model one embodiment.
Detailed description of the invention
In conjunction with the drawings and specific embodiments, this utility model is described in further detail.
As shown in Figure 1, a kind of intermittent pulse aerator being applied to water remediation, including the aeration being arranged under water Structure 1, aeration structure 1 connects the gas-supplying structure 2 of oriented aeration structure 1 supply, uses air compressor machine or blower fan;Aeration structure 1 The aeration opening managed including conveying and be arranged on conveying pipe, aeration opening is provided with tapered micro holes aeration board, and micropore size is 0.1- 0.5mm, the present embodiment selects 0.2mm.In order to realize intermittent aerating, it is provided with control between gas-supplying structure 2 and aeration structure 1 and exposes The control structure 3 of the intermittent aeration of depressed structure 1.Control structure 3 includes the sealing cavity 31 connected with gas-supplying structure 2, annular seal space Body 31 arranges gas outlet, arranges pressure-control valve 4 at gas outlet, seals cavity 31 and is connected with aeration structure 1 by gas outlet.Control Structure 3 processed sets the housing 32 sealing cavity 31 in including, be provided with volume regulating part 33 in cavity 31, for adjustment disk 331 and control The telescopic cylinder 332 that adjustment disk 331 processed moves up and down, the outer ring of adjustment disk 331 is provided with sealing ring, adjustment disk 331 and control The inner wall sealing of structure housing 32 processed connects, and controls to seal the volume of cavity by the position of adjustment disk 331, thus between controlling Have a rest intermittent time of aeration.

Claims (7)

1. it is applied to an intermittent pulse aerator for water remediation, including the aeration structure (1) being arranged under water, its feature Being, described aeration structure (1) connects the gas-supplying structure (2) that oriented described aeration structure (1) supplies, described gas-supplying structure (2) And being provided with the control structure (3) controlling the intermittent aeration of aeration structure (1) between described aeration structure (1), described control is tied Structure (3) includes the sealing cavity (31) connected with described gas-supplying structure (2), and described sealing cavity (31) arranges gas outlet, described Arranging control valve (4) at gas outlet, described sealing cavity (31) is connected with described aeration structure (1) by described gas outlet.
Intermittent pulse aerator the most according to claim 1, it is characterised in that described gas-supplying structure (2) be air compressor machine or Person's blower fan.
Intermittent pulse aerator the most according to claim 1, it is characterised in that described aeration structure (1) includes conveying pipe With the aeration opening being arranged on described conveying pipe, described aeration opening is provided with aeration board.
Intermittent pulse aerator the most according to claim 1, it is characterised in that described control structure (3) sets close in including The housing (32) of envelope cavity (31), is provided with volume regulating part (33) in described cavity (31).
Intermittent pulse aerator the most according to claim 3, it is characterised in that described aeration board is tapered micro holes aeration Plate.
Intermittent pulse aerator the most according to claim 5, it is characterised in that the micropore hole of described tapered micro holes aeration board Footpath is 0.1-0.5mm.
Intermittent pulse aerator the most according to claim 4, it is characterised in that described volume regulating part (33) is adjustment disk (331) and control described adjustment disk (331) telescopic cylinder (332) that moves up and down, the outer ring of described adjustment disk (331) is arranged Sealing ring, described adjustment disk (331) is had to be connected with the inner wall sealing of described control structure housing (32).
CN201620091110.8U 2016-01-29 2016-01-29 Be applied to water body remediation's intermittent type pulse aeration equipment Active CN205556252U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201620091110.8U CN205556252U (en) 2016-01-29 2016-01-29 Be applied to water body remediation's intermittent type pulse aeration equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201620091110.8U CN205556252U (en) 2016-01-29 2016-01-29 Be applied to water body remediation's intermittent type pulse aeration equipment

Publications (1)

Publication Number Publication Date
CN205556252U true CN205556252U (en) 2016-09-07

Family

ID=56821607

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201620091110.8U Active CN205556252U (en) 2016-01-29 2016-01-29 Be applied to water body remediation's intermittent type pulse aeration equipment

Country Status (1)

Country Link
CN (1) CN205556252U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109399880A (en) * 2017-08-18 2019-03-01 天津大学 A kind of pulsed microbial inoculum/adding of agent synchronization aeration oxygenator

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109399880A (en) * 2017-08-18 2019-03-01 天津大学 A kind of pulsed microbial inoculum/adding of agent synchronization aeration oxygenator

Similar Documents

Publication Publication Date Title
CN103739082B (en) The system of artificial flowing aeration coupled biological film floating bed purifying eutrophication water body
CN102276068B (en) River channel ecological construction and water body restoring system
CN105621789B (en) A kind of biogas slurry treatment device and method based on microdisk electrode
CN105585223B (en) A kind of freshwater aquiculture waste water advanced treatment recovery system and method
CN102464404B (en) Method and system for remediation and treatment of polluted river water
CN102718326B (en) Water eco-purification system and purification method thereof
CN207091218U (en) A kind of livestock breeding wastewater advanced treatment system
CN109197735A (en) A kind of circulating water aquiculture system
CN109052834A (en) A kind of administering method of eutrophication water
CN104787987A (en) Device and method for using industrial wastes to control lake eutrophication
CN207645912U (en) A kind of device of high efficiency purifying eutrophic water quality
CN205556252U (en) Be applied to water body remediation's intermittent type pulse aeration equipment
CN104876330A (en) Aerobic granular sludge system construction and operation method for treating culture biogas slurry
CN204897635U (en) City lake eutrophy controlling means
CN202038919U (en) Riverway ecology construction and water restoration system
CN203568903U (en) Ecological floating bed with artificial meadow
CN111689640A (en) Sewage treatment method
CN104150605A (en) Floating island type complex organism river purifier
CN201268619Y (en) Efficient free ecological radical capable of being used under multiple water environments
CN101323496B (en) Scale hogpen sewage disposal method and integrated equipment thereof
Xiao et al. Marine factory farming techniques and equipment
CN109399859A (en) A kind of sewage disposal system using electrolysis method joint biological treatment
CN103588302B (en) Artificial-meadow ecological floating bed
CN208577510U (en) A kind of microkinetic combined film bioreactor
CN207175693U (en) Countryside sewage treatment equipment

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
C41 Transfer of patent application or patent right or utility model
TR01 Transfer of patent right

Effective date of registration: 20161214

Address after: 313000 Industrial Road, Taihu, Huzhou, Zhejiang high tech Industrial Park, Wuxing District, No.

Patentee after: ZHEJIANG JUNE-5 ENVIRONMENT TECHNOLOGY CO., LTD.

Address before: 313000 Industrial Road, Taihu, Huzhou, Zhejiang high tech Industrial Park, Wuxing District, No.

Patentee before: ZHEJIANG WEITAN TECHNOLOGY CO., LTD.

Patentee before: ZHEJIANG JUNE-5 ENVIRONMENT TECHNOLOGY CO., LTD.

CB03 Change of inventor or designer information

Inventor after: Xu Ting

Inventor after: Liang Xinqiang

Inventor after: Li Yucai

Inventor after: Zhou Qi

Inventor after: Yu Zhongli

Inventor before: Xu Ting

Inventor before: Liang Xinqiang

Inventor before: Shen Chaofeng

Inventor before: Li Yucai

Inventor before: Zhou Qi

Inventor before: Yu Zhongli

CB03 Change of inventor or designer information
CP01 Change in the name or title of a patent holder

Address after: 313000 Industrial Road, Taihu, Huzhou, Zhejiang high tech Industrial Park, Wuxing District, No.

Patentee after: Zhejiang green environment Limited by Share Ltd

Address before: 313000 Industrial Road, Taihu, Huzhou, Zhejiang high tech Industrial Park, Wuxing District, No.

Patentee before: ZHEJIANG JUNE-5 ENVIRONMENT TECHNOLOGY CO., LTD.

CP01 Change in the name or title of a patent holder
TR01 Transfer of patent right

Effective date of registration: 20200824

Address after: 313000 105, room 2, Pu an road, Donglin Town, Wuxing District, Huzhou, Zhejiang, China, 50

Patentee after: ZHEJIANG METHYL SOURCE LIFE TECHNOLOGY Co.,Ltd.

Address before: 313000 Industrial Road, Taihu, Huzhou, Zhejiang high tech Industrial Park, Wuxing District, No.

Patentee before: ZHEJIANG JUNE5 ENVIRONMENT TECH Co.,Ltd.

TR01 Transfer of patent right