CN206014622U - A kind of river regulation repair system of utilization artificial aquatic weed formula film silk - Google Patents
A kind of river regulation repair system of utilization artificial aquatic weed formula film silk Download PDFInfo
- Publication number
- CN206014622U CN206014622U CN201621028817.0U CN201621028817U CN206014622U CN 206014622 U CN206014622 U CN 206014622U CN 201621028817 U CN201621028817 U CN 201621028817U CN 206014622 U CN206014622 U CN 206014622U
- Authority
- CN
- China
- Prior art keywords
- film silk
- aquatic weed
- artificial aquatic
- formula
- river regulation
- 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 - Fee Related
Links
- 241000196324 Embryophyta Species 0.000 title claims abstract description 33
- 230000008439 repair process Effects 0.000 title claims abstract description 17
- 230000033228 biological regulation Effects 0.000 title claims abstract description 15
- 238000005273 aeration Methods 0.000 claims abstract description 18
- 238000001914 filtration Methods 0.000 claims abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 25
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 3
- 239000012510 hollow fiber Substances 0.000 claims description 3
- 239000000463 material Substances 0.000 claims description 3
- 229920005597 polymer membrane Polymers 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 2
- 230000005611 electricity Effects 0.000 claims 1
- 238000010276 construction Methods 0.000 abstract description 4
- 239000010802 sludge Substances 0.000 abstract description 4
- 230000010354 integration Effects 0.000 abstract description 3
- 238000012423 maintenance Methods 0.000 abstract description 3
- 244000005700 microbiome Species 0.000 description 8
- 239000001301 oxygen Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 230000000694 effects Effects 0.000 description 5
- 238000000034 method Methods 0.000 description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 239000010410 layer Substances 0.000 description 4
- 230000008569 process Effects 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 230000007774 longterm Effects 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 230000007704 transition Effects 0.000 description 2
- 238000003911 water pollution Methods 0.000 description 2
- 241000195493 Cryptophyta Species 0.000 description 1
- 241001453382 Nitrosomonadales Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 230000002159 abnormal effect Effects 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 210000000476 body water Anatomy 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000009294 enhanced biological phosphorus removal Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000000796 flavoring agent Substances 0.000 description 1
- 235000019634 flavors Nutrition 0.000 description 1
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 239000002346 layers by function Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 230000000050 nutritive effect Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 239000000126 substance 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
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Biological Treatment Of Waste Water (AREA)
Abstract
This utility model is related to a kind of river regulation repair system of utilization artificial aquatic weed formula film silk, including filtration system, blast aeration system, photovoltaic generating system and film silk system, film silk system includes the multiple film silk components being sequentially connected, film silk system is connected with filtration system, the aeration blower of blast aeration system is connected with photovoltaic generating system, film silk component includes that film silk fixed support and the artificial aquatic weed formula film silk being fixed thereon, film silk fixed support are connected with the supply air line of blast aeration system.The river regulation repair system of the utilization artificial aquatic weed formula film silk that this utility model is provided, simple structure, easy construction, without the need for civil engineering, and sludge yield is few, can not spoil disposal, integration engineering investment less, be easy to maintenance management, hardly with safeguard, operating cost is relatively low, can meet the needs of practical application well.
Description
Technical field
This utility model belongs to technical field of water body purification, and in particular to control in a kind of river course of utilization artificial aquatic weed formula film silk
Reason repair system.
Background technology
At present, China's rivers, lake and reservoir currently suffer from pollution, and are still developing rapidly.The Landscape River water in city
Body pollution is mainly the intrusion of polluter, the airborne dust, the intrusion of house refuse such as in natural rainfall, air, the river of long term accumulation
Bottom mud and the harmful substance of mud release.Lack necessary circulation plus water body, dissolved oxygen is too low, lacks aquatic animal, plantses
The environment of existence, makes water body gradually lose self-purification capacity, and it is long-term clear to add river bottom mud, make bed mud constantly release be decomposed into N,
The nutritive salt such as P, cause body eutrophication, water body gradually greening, algae to overgrow, ultimately result in " wawter bloom " phenomenon, produce abnormal flavour,
Easily black smelly.Water pollution exacerbates shortage of water resources, directly threatens the safety of drinking water and the health of the people, has influence on
Industrial and agricultural production and Crop securify.It is the essential measure for recovering to improve river course basic function to carry out river course comprehensive improvement, is to carry
High water resources carrying capacity, the effective way that improves the ecological environment is the desirability of Green ecological riverway.
With regard to urban river water water quality itself, traditional sewage disposal technology can be effectively treated to which.But river so far
Road administer can only desilting the reason for change water, be that conventional art has engineering construction in this special sewage carrier in the face of river course
On be difficult to the bottleneck broken through, it is impossible in every river course Bian Doujian sewage treatment plant.The pollution treatment technology of pasture and water is planted in river course,
The river course that part river bed is soil property can only be adapted to, and be difficult to ensure that effect；And most of urban landscape rivers are all cultures
River bed, it is difficult to grow pasture and water.The methods such as treatment agent, instant effect is thrown in river course, but sustainability is poor, especially for
The river of flowing.Regular delivering medicament is needed, expense is too high, do not possess economic serviceability.
Utility model content
For above-mentioned problems of the prior art, the purpose of this utility model is that providing one kind can avoid the occurrence of
State the river regulation repair system of the utilization artificial aquatic weed formula film silk of technological deficiency.
In order to realize above-mentioned utility model purpose, the technical scheme that this utility model is provided is as follows：
A kind of river regulation repair system of utilization artificial aquatic weed formula film silk, including filtration system, blast aeration system, light
Photovoltaic generating system and film silk system, film silk system include the multiple film silk components being sequentially connected, film silk system and filtration system phase
Connection, the aeration blower of blast aeration system is connected with photovoltaic generating system, film silk component include film silk fixed support with
The artificial aquatic weed formula film silk being fixed thereon, film silk fixed support are connected with the supply air line of blast aeration system.
Further, filtration system includes screen mat.
Further, artificial aquatic weed formula film silk is hollow fiber polymer membrane.
Further, the structure ecto-entad of artificial aquatic weed formula film silk is followed successively by biomembrane 1, membranous wall 2, film inner chamber 3.
Further, film silk fixed support is made using polrvinyl chloride material.
Further, photovoltaic generating system includes solar module, controller, accumulator and AC inverter.
The river regulation repair system of the utilization artificial aquatic weed formula film silk that this utility model is provided, simple structure, construction party
Just, without the need for civil engineering, and sludge yield is few, can not spoil disposal, integration engineering investment less, be easy to maintenance management, almost
Without safeguarding, operating cost is relatively low, can meet the needs of practical application well.
Description of the drawings
Fig. 1 is structured flowchart of the present utility model；
Cross section structure diagrams of the Fig. 2 for artificial aquatic weed formula film silk；
Fig. 3 is the partial enlarged drawing of the part A in Fig. 2；
Fig. 4 is the hierarchy schematic diagram of the microorganism species for being attached to artificial aquatic weed film silk；
In figure, 1- biomembranes, 2- membranous walls, 3- film inner chambers, 4- aerobic nitrification layers, 5- transition zones, the anti-oxygen of 6- nitrify layer.
Specific embodiment
In order that the purpose of this utility model, technical scheme and advantage become more apparent, below in conjunction with the accompanying drawings and specifically
Embodiment is described further to this utility model.It should be appreciated that specific embodiment described herein is only in order to explaining this reality
With new, it is not used to limit this utility model.Embodiment in based on this utility model, those of ordinary skill in the art are not having
There is the every other embodiment obtained under the premise of making creative work, belong to the scope of this utility model protection.
As shown in figure 1, a kind of river regulation repair system of utilization artificial aquatic weed formula film silk, including filtration system, air blast
Aerating system, photovoltaic generating system and film silk system, film silk system include the multiple film silk components being sequentially connected, film silk system with
Filtration system is connected, and the aeration blower of blast aeration system is connected with photovoltaic generating system, and film silk component includes film silk
Fixed support and the artificial aquatic weed formula film silk being fixed thereon, film silk fixed support are connected with the supply air line of blast aeration system
Connect.Filtration system includes screen mat.
Film silk fixed support is made using polrvinyl chloride material.
Photovoltaic generating system includes solar module, controller, accumulator and AC inverter.
When mounted, screen mat is had made to order according to river sectional area size, horizontal is fixed on riverbed；Film silk fixed support is solid
River bed is placed on metal structure framework, firm firm, flood impact can be resisted；Artificial aquatic weed formula film silk is fixed on film silk
On fixed support, float in water, laterally put in column in river course, and arranged in river course successively according to design, heavily contaminated
Region can suitably increase the density of film silk component；The river bed position that supply air line is placed in below artificial aquatic weed formula film silk, along riverbank
Cause aeration blower；Aeration blower is provided with rain shade device；Room can be set in place, and photovoltaic generating system is too
Positive energy battery component is may be provided at the top of room or both sides, and other devices and aeration blower are installed along with room.
Artificial aquatic weed formula film silk is hollow fiber polymer membrane.As shown in Figures 2 and 3, the structure of artificial aquatic weed formula film silk
Ecto-entad is followed successively by biomembrane 1, membranous wall 2, film inner chamber 3.The specific surface area of artificial aquatic weed formula film silk is big, may be up to 4000m2/
m3, with film as carrier can be as microorganism in less space growth provide abundance bond area, substantially increase list
Microorganism concn in bit space, improves unit volume disposal ability, strengthens anti impulsion load ability.The aeration in film inner chamber 3,
Oxygen and pollutant are transmitted in two lateral biomembranes 1 of biomembrane 1 respectively and are consumed, and make attachment on artificial aquatic weed formula film silk
Biomembrane 1 has special hierarchy.
It is illustrated in figure 4 the hierarchy schematic diagram of the microorganism species for being attached to artificial aquatic weed film silk.Microorganism species
Apposition growth, forms aerobic nitrification layer 4, transition zone 5 and anti-oxygen nitrification layer 6 on biomembrane 1, and hydraulic detention time and biology stop
The time is stayed to can achieve independent control, the microorganism on biomembrane 1 will not be lost in current, and sludge retention time (SRT) is in theory
Endless can be considered as, this is growth generation time is longer, growth rate is slower microorganism, such as nitrifier, denitrifying bacterium, poly-
Phosphorus bacterium and anaerobic ammonia oxidizing bacteria etc. are there is provided growth and the possibility of enrichment.Meanwhile, the hierarchy of biomembrane 1 can be created
Occur while oxygen process and anaerobic processes, be that simultaneous nitrification-denitrification and Enhanced Biological Phosphorus Removal process provide possibility.
Treatment effect of the present utility model is as follows：
For the water body of flow velocity relatively slow (between 0-0.2m/s), the time of staying of the water body in repair system is longer,
Processing speed is more stable, and film silk component can disperse to lay, and is emitted in column in water body at certain intervals；
For the water body of flow velocity very fast (between 0.2-0.5m/s), can be in the intensive discharge open type film silk group in front end
Part；Subsequently laterally put in column in river course using artificial aquatic weed formula film silk, a small amount of interspersed addition open type film silk component, to increase
Blooming area.The purpose of wherein design front end open type film silk component is the treatment effect for strengthening just section, and intercepts entrance process
The impurity of section is to keep the cleaning of the water surface, while be lifted at the water body water yield and being significantly increased or system during unexpected water pollution event occur
The impact resistance of system.
This utility model is a long-term Water Ecological Recovery system, and wherein microbial film is pollutant in degraded water body
Functional layer.Microorganism colonization is the oxygen flow+attachment characteristic using film silk itself so as to natural membrane in river course；The biofilm time
According to water quality, flow velocity, water temperature concrete condition from two weeks to 3 months, can tend towards stability after biofilm success operation quickly,
V class or IV class water requirement is progressivelyed reach, and can continue efficiently and stably to maintain river water body treatment effect.
The river regulation repair system of the utilization artificial aquatic weed formula film silk that this utility model is provided, simple structure, construction party
Just, without the need for civil engineering, and sludge yield is few, can not spoil disposal, integration engineering investment less, be easy to maintenance management, almost
Without safeguarding, operating cost is relatively low, can meet the needs of practical application well.
Embodiment described above only expresses embodiment of the present utility model, and its description is more concrete and detailed, but simultaneously
Therefore the restriction to this utility model the scope of the claims can not be interpreted as.It should be pointed out that the ordinary skill for this area
For personnel, without departing from the concept of the premise utility, some deformations and improvement can also be made, these belong to this
The protection domain of utility model.Therefore, the protection domain of this utility model patent should be defined by claims.
Claims (6)
1. a kind of river regulation repair system of utilization artificial aquatic weed formula film silk, it is characterised in that expose including filtration system, air blast
Gas system, photovoltaic generating system and film silk system, film silk system include the multiple film silk components being sequentially connected, film silk system and mistake
Filter system is connected, and the aeration blower of blast aeration system is connected with photovoltaic generating system, and film silk component includes that film silk is solid
Fixed rack and the artificial aquatic weed formula film silk being fixed thereon, film silk fixed support are connected with the supply air line of blast aeration system
Connect.
2. the river regulation repair system of utilization artificial aquatic weed formula film silk according to claim 1, it is characterised in that filter
System includes screen mat.
3. the river regulation repair system of utilization artificial aquatic weed formula film silk according to claim 1, it is characterised in that artificial
Pasture and water formula film silk is hollow fiber polymer membrane.
4. the river regulation repair system of utilization artificial aquatic weed formula film silk according to claim 1, it is characterised in that artificial
The structure ecto-entad of pasture and water formula film silk is followed successively by biomembrane (1), membranous wall (2), film inner chamber (3).
5. the river regulation repair system of utilization artificial aquatic weed formula film silk according to claim 1, it is characterised in that film silk
Fixed support is made using polrvinyl chloride material.
6. the river regulation repair system of utilization artificial aquatic weed formula film silk according to claim 1, it is characterised in that photovoltaic
Electricity generation system includes solar module, controller, accumulator and AC inverter.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201621028817.0U CN206014622U (en) | 2016-08-31 | 2016-08-31 | A kind of river regulation repair system of utilization artificial aquatic weed formula film silk |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201621028817.0U CN206014622U (en) | 2016-08-31 | 2016-08-31 | A kind of river regulation repair system of utilization artificial aquatic weed formula film silk |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN206014622U true CN206014622U (en) | 2017-03-15 |
Family
ID=58259132
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201621028817.0U Expired - Fee Related CN206014622U (en) | 2016-08-31 | 2016-08-31 | A kind of river regulation repair system of utilization artificial aquatic weed formula film silk |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN206014622U (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107585865A (en) * | 2017-11-02 | 2018-01-16 | 安徽华骐环保科技股份有限公司 | A kind of new microbubble is oxygenated biological film wire and method for treating water |
| CN108558017A (en) * | 2018-03-30 | 2018-09-21 | 中冶华天工程技术有限公司 | Composite river wet land system for river corridor restoration |
-
2016
- 2016-08-31 CN CN201621028817.0U patent/CN206014622U/en not_active Expired - Fee Related
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107585865A (en) * | 2017-11-02 | 2018-01-16 | 安徽华骐环保科技股份有限公司 | A kind of new microbubble is oxygenated biological film wire and method for treating water |
| CN108558017A (en) * | 2018-03-30 | 2018-09-21 | 中冶华天工程技术有限公司 | Composite river wet land system for river corridor restoration |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102874934A (en) | Technology for direct in-situ treatment and ecological restoration of polluted water body | |
| CN105502803A (en) | Black and odorous river comprehensive treatment and ecological restoration method | |
| CN105645677A (en) | Horizontal flow/vertical flow integrated artificial wetland and operation method thereof | |
| CN103524006B (en) | Urban inland river rainfall runoff purification suspended wall self-oxygenating subsurface wetland device | |
| CN205442798U (en) | Green ecological chinampa device | |
| CN101857336A (en) | Water recycling circulating system | |
| CN205011472U (en) | Ecological comprehensive control system of open water | |
| CN206014622U (en) | A kind of river regulation repair system of utilization artificial aquatic weed formula film silk | |
| CN206308127U (en) | A kind of floating wetland for purifying landscape water body | |
| CN101941777B (en) | Method for treating sewage and ecologically restoring water environment of villages and small towns in water network region | |
| CN105417699A (en) | Vertical flow artificial wetland ecological degradation method for tail water of urban sewage treatment plant | |
| CN208561850U (en) | A kind of Micro-power cycle reoxygenation formula artificial floating island | |
| CN104563266A (en) | Rural domestic sewage high-ridge rice field irrigation regulation control system and construction method thereof | |
| CN104326574B (en) | The horizontal subsurface flow wetland system of strengthening micropollutant water denitrogenation in winter | |
| CN213416428U (en) | Adjustable and controllable efficient denitrification wetland system with self-supplied carbon source | |
| CN211896515U (en) | Artificial wetland system applied to super-limit purification treatment of low-concentration polluted water body | |
| CN210505956U (en) | Buried type synchronous river sewage treatment and ecological bank protection structure | |
| CN101891348B (en) | Sewage treatment system for water shortage cities and storage and advanced treatment method of sewage and rainwater | |
| CN204237622U (en) | A kind of horizontal subsurface flow wetland system strengthening micropollutant water denitrogenation in winter | |
| CN105347498A (en) | Establishing, starting and stable running method for tail water deep purification wetland | |
| CN104692598A (en) | Ecological treatment device for supplying recycled water to landscape water | |
| CN210491838U (en) | Multi-ecological-position aquatic plant community construction device | |
| CN112759087A (en) | Denitrification artificial wetland integrated purification system and sewage ecological purification method | |
| CN207159020U (en) | A kind of non-powered domestic sewage treatment device | |
| CN107235558B (en) | Ecological construction method of FBR biological bed, low-algae and low-turbidity water body and water body restoration system |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170315 |