CN209583907U - A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous - Google Patents
A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous Download PDFInfo
- Publication number
- CN209583907U CN209583907U CN201920095504.4U CN201920095504U CN209583907U CN 209583907 U CN209583907 U CN 209583907U CN 201920095504 U CN201920095504 U CN 201920095504U CN 209583907 U CN209583907 U CN 209583907U
- Authority
- CN
- China
- Prior art keywords
- water body
- water
- area
- aquatic
- plant
- 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
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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/22—Improving land use; Improving water use or availability; Controlling erosion
Abstract
A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous, including, interconnected water body purification area and aquatic ecological Landscape Region；Pollution sources primary precipitation purifying area, water source secondary stage purified area, water source three-level purifying area are set gradually in water body purification area；It is equipped with multiple wetlands in pollution sources primary precipitation purifying area and is percolated island；Water source sets floating wetland in secondary stage purified area；Submerged forest is set in water source three-level purifying area；The outlet that water body purification area is connected to aquatic ecological Landscape Region sets wetland diafiltration island, floating wetland；Aquatic plant system is set in aquatic ecological Landscape Region and the aquatic animal that swims；End sets immersible pump in aquatic ecological Landscape Region and pipeline is connected to water body purification area.The utility model integrates the control of contaminating endogenous source, face source contact scar source intercept process and the purification of exogenous pollution source, keep water body limpid, and be suitable for aquatic plants growth, not only ensure effects of purification quality, but also taken into account the recovery of landscape effect and native country aquatic plant system.
Description
Technical field
It is the utility model relates to Garden Engineering, in particular to a kind of to repair the artificial of super eutrophic water body and contaminating endogenous
Wetland construction.
Background technique
With the continuous improvement of people's living condition, requirement of the city dweller to living quality and living environment is increasingly
Height, the landscape water body of limpid beauty have become the pith of beautification people's lives environment.Landscape water body not only has ecology
Value, and adjustable temperature and humidity purify air, enhance comfort.But water quality of landscape water is more demanding, is mostly
Static or poor fluidity, self-purification capacity is poor, leads to that water will be changed at regular intervals, some directlys adopt tap water, not only
Waste water resource also takes time and effort.
On the other hand, modern city is leading with reinforced concrete structure, and hardening ratio is high, and rainwater can descend naturally impregnation to fill
Underground water occupies a narrow space, and surface runoff increases when causing to rain, and sea is seen in various regions when heavy rain, and flood control flood control pressure is big.In order to change
This status, 2012, sponge city concept was suggested for the first time.So-called sponge city refers to that city can have as sponge
" elasticity ", water suction, water storage, infiltration, water purification when raining by the water stored " release " and are used when needing, and promotion city is given birth to
State system function reduces the generation of Urban Flood Waterlogging.City " cavernous body " both includes the water systems such as river, lake, pond, also includes green
Ground, garden, city auxiliary facility as permeable road surface.
Both mitigate sewerage system using Landscape Water System as cavernous body using rainwater as the water source of landscape water body
Pressure, and make full use of rainwater resource.
But urban rainwater, since rainwash to the shower in city and washes away, water quality is poor, also referred to as face source is dirty
Dye.City surface source pollution object derives from urban surface deposit, includes broken snow (municipal refuse, animal wastes, the city of solid waste
Construction place deposit), the chemicals fertilizer and pesticide of application (lawn), Air settlement and vehicle emission etc..Rain
Water should be by purification before being used for landscape water body.
Conventional rainwater treatment is will to concentrate to carry out physics, chemical treatment after rainwater-collecting to reservoir, to remove rainwater
In pollutant.
The processing technique used for landscape water body mainly has aeration aerating method, physico-chemical process, chemistry to kill algae sterilization, biochemistry
Facture, ecological method etc..
In urban redevelopment, in order to promote City Life Quality, the shallower industrial sites of many pollution levels or mine
It is converted for urban green space.The reasonability done so is: can be put into the smallest soil, promote environment matter to the greatest extent
Urban green space structure is measured and improved, realizes urban sustainable development.In the maximum that contaminated site development & construction water landscape encounters
Challenge is endogenous pollution.Endogenous pollution is primarily referred to as coming the pollutant in bed mud, including and is not limited to organic matter, nitrogen, phosphorus, a huge sum of money
Belong to etc..Heavy metal, pathogenic agent in bed mud by river and landscape pond association of plants and animals and microbiologic population generate
Negative effect, destroys the integrality of the entire ecosystem, to influence its function, is unfavorable for the performance of water body self-purification ability.In
When temperature increases, a large amount of nitrogen phosphorus substances of sediment release cause water eutrophication.
Utility model content
The purpose of this utility model is to provide a kind of artificial swamp structures for repairing super eutrophic water body and contaminating endogenous
It makes, integrates the control of contaminating endogenous source, face source contact scar source intercept process and the purification of exogenous pollution source, keep water body limpid, and
It is suitable for aquatic plants growth, reaches lasting and purify water and view exhibition effect.
To achieve the above purpose, the technical solution of the present invention is:
A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous comprising, interconnected water body
Purifying area and aquatic ecological Landscape Region；
The water body purification area is equipped with the import flowed into from rainwater, outer river water and aquatic ecological Landscape Region recirculation water and water
The outlet of ecoscape area connection is given birth to, pollution sources primary precipitation is set gradually from import to outlet in the water body purification area and purifies
Area, water source secondary stage purified area and water source three-level purifying area；Wherein, at least one is equipped in the pollution sources primary precipitation purifying area
Wetland is percolated island；Floating wetland is equipped in water source secondary stage purified area；Submerged forest is equipped in the water source three-level purifying area；
The outlet that the water body purification area is connected to aquatic ecological Landscape Region is arranged a wetland and is percolated island and a floating wetland；
Aquatic plant system in the aquatic ecological Landscape Region equipped with constructive species and the aquatic animal that swims are formed gloomy in water
Woods；And end sets immersible pump in aquatic ecological Landscape Region and pipeline is connected to the entrance in the water body purification area；
Aerator is respectively equipped in the water body purification area and aquatic ecological Landscape Region, it is preferred that the water body purification area
Fountain aerator is inside set, aquatic ecological Landscape Region sets water carrying type aerator；
The water body purification area and aquatic ecological Landscape Region are along revetment setting vegetation system.
Preferably, Different Nutrition salt level of the aquatic plant system in the water body purification area according to three-level purifying area,
Successively from most resistant to pollution mushroom grass, to resistant to pollution emergent aquactic plant, then to more resistant to pollution grass of escaping from water.
Preferably, water body purification area revetment is configured pollution of area source pooling zone, is arranged inside and intercepts irrigation canals and ditches and interception
Dam, sedimentation intercept place runoff bring pollution of area source.
Preferably, the aquatic plant system for the constructive species being arranged in the aquatic ecological Landscape Region includes the heavy water of oligotrophic type
Plant, such as eel grass or hydrilla verticillata.
Preferably, the structure on wetland diafiltration island includes: that ecology bag encloses slope protection layer, encloses structure using woven bag,
Form an accommodating space；Filling gravel and haydite in the woven bag；It is viscous that mineral are followed successively by the accommodating space from top to bottom
Soil layer, haydite layer and gravel layer；Emergent aquactic plant is set at the top of the gravel layer.
It further, further include a basal layer, the ecology bag encloses slope protection layer and is set on the basal layer, the basis
Layer includes rubble or/and cobble.
Preferably, the planting density of the emergent aquactic plant is 9~25 plants/m2；The emergent aquactic plant include: reed, the stem or leaf of cattail,
Water chestnut, Chinese celery, Scirpus tabernaemontani, wild rice stem, cattail, Lythrum salicaria, calamus, water Radix Ophiopogonis, cyperus alternifolius or rush.
Preferably, the floating wetland include: as floating wetland frame and support matrix module, be filled in matrix
Filler module, plantation in module is in the wetland plant in filler module.
Preferably, the vegetation system includes: successively to plant terrestrial plant from bank to pool center, hygrophyte, endure
Water plant, floating plant, submerged plant.
Preferably, bottom is bottom-up in the aquatic ecological Landscape Region sets gradually filling attapulgite or zeolite powder
Ecology bag, planting soil.
In the design of the utility model artificial swamp construction:
The connection of water body purification area aquatic ecological Landscape Region, the water in water body purification area flows automatically to aquatic ecological Landscape Region, aquatic
Immersible pump is arranged in ecoscape area end, and water is back to water body purification area front end.The water of aquatic ecological Landscape Region is also for region
Interior greening and car washing water.Rainwater is discharged into water body purification area after rain pipe summarizes, and in order to keep man-made lake stable level, needs
It is supplemented from outer river diversion, outer river water is lifted into water body purification area through self priming pump.In rainwater, outer river water and aquatic ecological landscape
Area's recirculation water enters pool position and a diafiltration island is respectively arranged.Rainwater, outer river water and aquatic ecological Landscape Region recirculation water are first through seeping
It filters island and intercepts filtering, then successively reached and aquatic ecological Landscape Region junction by floating wetland, submerged forest.To increase lake water
A fountain aerator is arranged in water body purification area for dissolved oxygen.
From purification of water quality angle, water body purification divides into pollution sources primary precipitation purifying area, water source secondary stage purified area and water
Source three-level purifying area.By the purified water body of three-level, it is able to enter aquatic ecosystem substantially and restores show area (aquatic ecological
Landscape Region) water body reach oligotrophic type submerged plant existence standard (transparency > 60cm, TP < 0.15mg/L).
The water body purification area configures different aquatic plants from inlet to the exit being connected to aquatic ecological Landscape Region
Object system, from most resistant to pollution mushroom grass, to resistant to pollution emergent aquactic plant, then to more resistant to pollution grass of escaping from water.
The diafiltration island primary structure is that woven bag encloses layer, mineral clay layer, haydite layer and gravel layer etc., and is being percolated
Emergent aquactic plant is planted at the top of island.It mainly passes through mineral clay layer, haydite layer and gravel layer to the percolation of tail water and endures
Water plant removes a part of pollutant, while intercepting water body recovery technology, promotes water transparency.
Water body purification area and aquatic ecological Landscape Region connectivity part are provided with a diafiltration island and row's mouth floating wetland.It is floating
Dynamic wetland includes filler module, matrix module, wetland plant, and the floating wetland and root system of plant of modularized design have adsorbed largely
Microorganism forms biomembrane, and when sewage flows through floating wetland root area, pollutant is by matrix module, root system of plant and micro- life
It is removed under the collective effect of object.The biomembrane retention that a large amount of solid suspension is adhered in matrix and root system of plant；Have
Machine pollutant is decomposed by the respiration of microorganism；The nutriments such as nitrogen phosphorus are absorbed by plants assimilation removal, simultaneously also by
The microbial processes such as nitrification, denitrification, poly- phosphorus remove in aerobic, anaerobic environment.
Vegetation system (such as PCA soil flexibility vegetation system) is arranged along revetment in water body purification area, is imported with intercepting by earth's surface
Rather than the rainwater non-point pollution of rain pipe confluence.PCA soil flexibility vegetation system can be consolidated by the development of vegetation root system
Soil slows down water velocity, and water conservation forms the cogeneration system between microorganism and vegetation system, plants by soil flexibility
The condition provided by system is able to mutual assistance between the environmental factors such as water, soil, vegetation, microorganism, restores impaired ecological environment.
Aquatic ecological Landscape Region bottom is to avoid heavy metal in bed mud, pathogenic agent to river and landscape pond
Association of plants and animals and microbiologic population have a negative impact, destroy the integrality of the entire ecosystem, to influence its function,
The ecology bag of one layer of filling attapulgite or zeolite powder is completely spread at aquatic ecological Landscape Region pool bottom, completely spreads a kind of planting soil thereon.
Attapulgite or zeolite powder are ideal adsorbents, can be decolourized, deodorization taste removal, removing heavy metals ion and carcinogen.
Since attapulgite or zeolite powder are seated in ecology bag, there are also a small amount of gap between ecology bag, water body is not complete with lakebed
Partition, can permeate on a small quantity with recharge of groundwater.Compared with the man-made lake of concrete hardening or laying HDPE film, not
It blocks water body to connect with the water body of lakebed soil, ensure that exchanging for lake water and underground water；Compared with natural mud bottom, attapulgite hybrid or
Zeolite powder man-made lake bottom can isolate the contaminating endogenous in original bed mud, and adsorb the pollution of artificial lacustrine deposits, slow down water body
Eutrophication process.
Compared with the prior art, the advantages of the utility model are:
1. being compared with traditional wetland recovery engineering
Traditional wetland recovery engineering is for the purpose of being restored by wetlands ecosystems, to focus on each ecological engineering area morphological feature and build
If resuming work with wetland plant system, generally not using purification of water quality as the main functionality of ecological wetland.
The utility model wetland reparation has taken into account the recovery of ecological wetland functional areas, the recovery of aquatic plant system and dirt
Packing, interception and the system purification in dye source are the optimization that current ecological wetland restores and artificial swamp combines as a result, protecting
Hinder effects of purification quality, and takes into account the recovery of landscape effect and native country aquatic plant system.
2. being compared with single recovery submerged vegetation engineering
Complete pollution interception, purification system are built in the utility model wetland reparation, and eco-functional regionalization is complete, wait continue
O&M and vegetation season come interim, it will complete purification of water quality, aquatic ecosystem recovery are presented, landscape water body area is in
The state of existing submerged forest.
3. being compared with conventional area source pollution purifying system
Conventional rainwater treatment is will to concentrate to carry out physics, chemical treatment after rainwater-collecting to reservoir, to remove rainwater
In pollutant.
After roof rain water collecting, polluted since rainwater is opposite smaller, general only need can after precipitating disinfection
In terms of being applied to the common production and living in city.Road rain water water quality due to road environment complexity, the contaminated degree of water quality compared with
Greatly, ingredient is also relatively complicated, firstly, need to consider early-stage rainwater stream abandoning, to carrying out coagulation, precipitating after subsequent rainwater-collecting again
With filtering etc. usual manners processing.The case where according to water quality, also needs to increase activated carbon adsorption treatment process when having to.
Conventional rainwater treatment technique are as follows: catchment-sieve/grid-storage pond-coagulative precipitation tank -- clear water reserviors-resource benefit
With.
This mature technology, but construction cost is high, the rainwater treatment facility vacant time is long, and input and output are low.
The utility model directly utilizes landscape water body purifying rainwater, and rainwater purification unit, construction cost is no longer separately provided
Low, no rainwater treatment facility is vacant, and input and output are high.
4. being compared with conventional landscape water body operating system
The processing technique used both at home and abroad for landscape water body at present mainly has aeration aerating method, physico-chemical process, chemistry to kill algae
Sterilization, biochemical treatment process, ecological method etc..
Water body aeration aerating method, which refers to, carries out artificial aeration to water body, to improve the dissolved oxygen content in water, builds aerobic
Bacterium living environment removes dissolved organic matter in water removal using microbial growth.The mode of aeration aerating have waterfall, drop,
Three kinds of water spray, the energy consumption of three kinds of methods is all very high, few 24 hours continuous operations.The effect of aeration aerating method is by life micro- in water body
The quantity and water pollutant type of object limit, and are used alone and are generally unable to reach long-term maintenance water quality purpose.
What physico-chemical process was often used has coagulant sedimentation, mixed condensed gas flotation process and filtration method etc..The object of physico-chemical process processing is water
In particulate matter, suspended matter and colloidal impurity etc..Physico-chemical process chemical agent reaches solid by the interception of gravity, buoyancy or filtrate
Liquid separates purpose, and solid impurity is removed from water body, and general setting bypass extracts landscape water section out, clear water flows back after processing
To landscape water body.Since many algae are small and light, physico-chemical process is bad to algae removal effect.
Chemical algae removing sterilization refers to that direct Xiang Shuizhong adds algicide, kills algae, inhibits alga eruption, has technique
Simply, the advantages that initial investment saves.Algicide is commonly used just like copper sulphate, bleaching powder, sodium hypochlorite etc..In all kinds of algicide, sulphur
Sour copper is preferable except algae effect, and drug effect is long, but cannot remove stink, and copper sulphate is toxic for fish.Bleaching powder or chlorine can
Stink is removed, but irritant smell itself, dosage are more difficult to control.Chemical algae removing sterilization can cause secondary pollution to environment,
And longtime running is at high cost.In view of the ornamental value of landscape water and the health of people, Ying Jinliang avoid using.
Biochemical treatment process refers generally to add microbial method, when content of organics is higher suitable for landscape water.That launches is micro-
Biology can be the engineering strain of laboratory cultures screening, be also possible to the indigenous strain using screening and culturing in landscape water body.
It is higher that operating cost is individually used for a long time, use is generally cooperateed with other methods.
Restoration of the ecosystem method is to be purified water using water plant and aquatic animal for guidance with ecological principle, utilize control
Water plant and planktonic algae amount processed.
The utility model safeguards landscape water body using wetland reparation, has taken into account recovery, the aquatic plant of ecological wetland functional areas
The recovery of object system and packing, interception and the system purification of pollution sources, have not only ensured effects of purification quality, but also taken into account landscape effect
The recovery of fruit and native country aquatic plant system.
Detailed description of the invention
Fig. 1 is the structural schematic diagram of the utility model embodiment.
Fig. 2 is the structural schematic diagram that wetland is percolated island in the utility model embodiment.
Specific embodiment
Referring to Fig. 1, a kind of super eutrophic water body of reparation of the utility model and the artificial swamp construction of contaminating endogenous,
Including interconnected water body purification area A and aquatic ecological Landscape Region B；
The water body purification area A is equipped with from rainwater (storm sewer 101), outer river water (outer river water pipeline 102) and aquatic life
The import of state Landscape Region recirculation water inflow, the outlet being connected to aquatic ecological Landscape Region B, the water body purification area A are interior from import
Pollution sources primary precipitation purifying area 10, water source secondary stage purified area 20 and water source three-level purifying area 30 are set gradually to outlet；Wherein,
A wetland, which is equipped with, in the pollution sources primary precipitation purifying area 10 is percolated island 1；It is equipped in water source secondary stage purified area 20 floating
Dynamic wetland 2, submerged forest 3；It is equipped with 4, wetlands of floating wetland in the water source three-level purifying area 30 and is percolated island 1 '；
It is equipped with the aquatic plant system 5 of constructive species in the aquatic ecological Landscape Region B, forms forest in water；And aquatic life
End sets immersible pump 6 in the B of state Landscape Region and pipeline 7 is connected to the entrance of the water body purification area A；
Aerator 8,8 ' is respectively equipped in the water body purification area A and aquatic ecological Landscape Region B, it is preferred that the water body
A is respectively equipped with fountain aerator in purifying area, and aquatic ecological Landscape Region B is equipped with water carrying type aerator；
Vegetation system 9,9 ' is arranged along revetment in the water body purification area A and aquatic ecological Landscape Region B.
Preferably, the aquatic plant system 9 in the water body purification area A includes successively mushroom grass, emergent aquactic plant, escapes from water
Grass.
Preferably, the water body purification area A revetment is configured pollution of area source pooling zone, is arranged inside and intercepts irrigation canals and ditches and interception
Dam, sedimentation intercept place runoff bring pollution of area source.
Preferably, the aquatic plant system for the constructive species being arranged in the aquatic ecological Landscape Region B includes that oligotrophic type is heavy
Water plant, such as eel grass population.
Referring to fig. 2, the structure on wetland diafiltration described in the utility model island 1 includes: that ecology bag encloses slope protection layer 11, using volume
It knits bag and encloses structure, form an accommodating space；Filling gravel and haydite in the woven bag；In the accommodating space from top to bottom
It is followed successively by mineral clay layer 12, haydite layer 13 and gravel layer 14；Emergent aquactic plant 15 is set to 14 top of gravel layer.
It further, further include a basal layer 16, the ecology bag encloses slope protection layer 11 and is set on the basal layer 16, described
Basal layer 16 include rubble or/and cobble.
Preferably, the planting density of the emergent aquactic plant 15 is 9~25 plants/m2；The emergent aquactic plant includes: reed, Pu
Grass, water chestnut, Chinese celery, Scirpus tabernaemontani, wild rice stem, cattail, Lythrum salicaria, calamus, water Radix Ophiopogonis, cyperus alternifolius or rush.
Preferably, the floating wetland 2 include as floating wetland frame and support matrix module, be filled in matrix
Filler module, plantation in module is in the wetland plant in filler module.
Preferably, the vegetation system 9 includes: successively to plant wild flower combination from bank to pool center, emergent aquactic plant, sink
Water plant, floating plant, submerged plant.
Preferably, bottom is bottom-up in the aquatic ecological Landscape Region sets gradually filling attapulgite or zeolite powder
Ecology bag, planting soil.
Claims (12)
1. a kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous, which is characterized in that including being interconnected
Water body purification area and aquatic ecological Landscape Region；
The water body purification area is equipped with the import and aquatic life flowed into from rainwater, outer river water and aquatic ecological Landscape Region recirculation water
The outlet of state Landscape Region connection, sets gradually pollution sources primary precipitation purifying area from import to outlet in the water body purification area,
Water source secondary stage purified area and water source three-level purifying area；Wherein, it is wet that at least one is equipped in the pollution sources primary precipitation purifying area
Ground is percolated island；Floating wetland is equipped in water source secondary stage purified area；Submerged forest is equipped in the water source three-level purifying area；Institute
It states the outlet that water body purification area is connected to aquatic ecological Landscape Region and one wetland diafiltration island and row's mouth floating wetland is set；
Aquatic plant system in the aquatic ecological Landscape Region equipped with constructive species and the aquatic animal that swims, form forest in water；
And end sets immersible pump in aquatic ecological Landscape Region and pipeline is connected to the entrance in the water body purification area；
Aerator is respectively equipped in the water body purification area and aquatic ecological Landscape Region；
The water body purification area and aquatic ecological Landscape Region are along revetment setting vegetation system.
2. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, which is characterized in that
Different Nutrition salt level of the aquatic plant system according to three-level purifying area in the water body purification area, successively from most resistant to pollution
Mushroom grass arrives resistant to pollution emergent aquactic plant, then to more resistant to pollution grass of escaping from water.
3. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, which is characterized in that
Water body purification area revetment is configured pollution of area source pooling zone, is arranged inside and intercepts irrigation canals and ditches and intercept dam, sedimentation intercepts place
Runoff bring pollution of area source.
4. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, which is characterized in that
The aquatic plant system for the constructive species being arranged in the aquatic ecological Landscape Region includes oligotrophic type submerged plant.
5. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as claimed in claim 4, which is characterized in that
The oligotrophic type submerged plant is eel grass or hydrilla verticillata.
6. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, which is characterized in that
Wetland diafiltration island includes:
Ecology bag encloses slope protection layer, encloses structure using woven bag, forms an accommodating space；In the woven bag filling gravel and
Haydite；Mineral clay layer, haydite layer and gravel layer are followed successively by the accommodating space from top to bottom；
Emergent aquactic plant is set at the top of the gravel layer.
7. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as claimed in claim 6, which is characterized in that
Further include a basal layer, the ecology bag encloses slope protection layer and is set on the basal layer, the basal layer include rubble or/and
Cobble.
8. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as claimed in claim 6, which is characterized in that
The planting density of the emergent aquactic plant is 9~25 plants/m2；The emergent aquactic plant include: reed, the stem or leaf of cattail, water chestnut, Chinese celery, Scirpus tabernaemontani,
Wild rice stem, cattail, Lythrum salicaria, calamus, water Radix Ophiopogonis, cyperus alternifolius or rush.
9. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, which is characterized in that
The floating wetland includes: the frame and the matrix module of support, the filler mould that is filled in matrix module as floating wetland
Block, plantation are in the wetland plant in filler module.
10. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, feature exists
In, the vegetation system include: successively planted from bank to aquatic ecological Landscape Region pool center terrestrial plant, hygrophyte,
Emergent aquactic plant, floating plant, submerged plant.
11. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, feature exists
In the bottom-up ecology bag for setting gradually filling attapulgite or zeolite powder in bottom, plantation in the aquatic ecological Landscape Region
Soil.
12. repairing the artificial swamp construction of super eutrophic water body and contaminating endogenous as described in claim 1, feature exists
In setting fountain aerator in the water body purification area, aquatic ecological Landscape Region sets water carrying type aerator.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201920095504.4U CN209583907U (en) | 2019-01-21 | 2019-01-21 | A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201920095504.4U CN209583907U (en) | 2019-01-21 | 2019-01-21 | A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN209583907U true CN209583907U (en) | 2019-11-05 |
Family
ID=68352894
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201920095504.4U Active CN209583907U (en) | 2019-01-21 | 2019-01-21 | A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN209583907U (en) |
-
2019
- 2019-01-21 CN CN201920095504.4U patent/CN209583907U/en active Active
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN106186343B (en) | A kind of comprehensive processing method to urban river | |
| CN101948214B (en) | Ecological greenbelt treatment process and system for treating rural domestic sewage | |
| CN103880257B (en) | The ecologic assemblage treatment process of a kind of rural area decentralized type sewage and device | |
| CN101723520B (en) | Method for cutting low-pollution water load of venous riverway | |
| CN105645675B (en) | A kind of smelly water bodies of rivers and lakes water quality high-efficient purification technology of urban black | |
| CN101811807B (en) | Black and odorous and eutrophication water body biological and ecological remediation and treatment process | |
| CN106746205A (en) | A kind of Intelligent rain purifies landscape system | |
| CN100595169C (en) | Ecological system for water purification and recover | |
| CN104986860A (en) | Ecological treatment technology for power-free river water purification | |
| CN101781061B (en) | Method for plant arrangement of vertical flow and horizontal subsurface flow combined artificial wetland | |
| CN1868926A (en) | Composite ecological treatment method of sewage for artificial wet land and its system | |
| CN108128967A (en) | A kind of river water body dystopy comprehensive high-efficiency processing method and system | |
| CN207243673U (en) | A kind of ecological water purification system for sponge city | |
| CN103058463B (en) | Continuous purifying system for bay water quality as well as treatment method and application thereof | |
| CN105461075A (en) | Urban runoff non-point source pollution advanced treatment and reuse technology | |
| CN109607975A (en) | A kind of artificial swamp construction for repairing super eutrophic water body and contaminating endogenous | |
| CN110092480A (en) | A kind of sinking land in coalmining areas administering method and water pollution control system | |
| CN200974793Y (en) | Sewage composite artificial marshland ecological treatment system | |
| CN207159053U (en) | Module type sewage processing system | |
| CN105601043B (en) | A kind of domestic sewage of villages and small towns ecology microkinetic processing system | |
| CN207435274U (en) | A kind of Heihe road cleaning treatment system | |
| CN207047066U (en) | A kind of domestic sewage of villages and small towns rural area landscape type total system | |
| CN205616732U (en) | Ecological clean system of farmland irrigation canals and ditches | |
| CN105254130A (en) | Wetland sewage treatment system and method thereof | |
| CN101475289B (en) | Reinforced biological reaction tank and reinforced undercurrent wetland processing system |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CP03 | Change of name, title or address | ||
| CP03 | Change of name, title or address |
Address after: 200063 Building 9, No. 1000, Caoyang Road, Putuo District, Shanghai Patentee after: Shanghai Construction Engineering Environmental Technology Co.,Ltd. Address before: 200331 Room 202, building 1, Lane 277, Yongdeng Road, Putuo District, Shanghai Patentee before: SHANGHAI ZHUOYU ENVIRONMENT ENGINEERING Co.,Ltd. |