CN206417916U - A kind of artificial wet land system for sewage treatment plant tail water advanced treating - Google Patents
A kind of artificial wet land system for sewage treatment plant tail water advanced treating Download PDFInfo
- Publication number
- CN206417916U CN206417916U CN201720026449.4U CN201720026449U CN206417916U CN 206417916 U CN206417916 U CN 206417916U CN 201720026449 U CN201720026449 U CN 201720026449U CN 206417916 U CN206417916 U CN 206417916U
- Authority
- CN
- China
- Prior art keywords
- water
- ecological pool
- plant
- ecological
- wet land
- 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
Abstract
A kind of artificial wet land system for sewage treatment plant tail water advanced treating, it is intended to overcome artificial marsh sewage treatment system treatment effeciency of the prior art low, the carbon source of sewage treatment plant tail water is not enough, cause the shortcoming that nitric efficiency is low, a kind of artificial wet land system is provided, also include the ecological cell system pre-processed to sewage, ecological cell system includes distributing channel, ecological pool and braiding channel, microbe carrier stuffing mounting bracket is provided with ecological pool pond body, microbe carrier stuffing is fixedly mounted in microbe carrier stuffing mounting bracket, the water surface of ecological pool is provided with plant floating bed, plant floating bed interior kind has emergent aquactic plant one, the water side of distributing channel and the water inlet end of ecological pool are connected, the water side of ecological pool and the water inlet end of braiding channel are connected, the water side of braiding channel is connected with the water inlet end of upper strata perforation sparge pipe.This practicality newly improve to the organic matter in sewage, nitrogen, phosphorus treatment effeciency, be adapted to processing sewage when use.
Description
Technical field
The utility model is related to advanced treatment of wastewater field, more particularly to a kind of for sewage treatment plant tail water advanced treating
Artificial wet land system.
Background technology
The form of export of China's municipal wastewater treatment plant tail water up to standard is mainly to concentrate discharge, and utilizes the self-purification capacity pair in river
Pollutant in tail water is further degraded, to meet the water environmental function target of receiving water body.But with urbanization process
Accelerate so that most tail water produced by municipal sewage treatment plant is received river and gradually loses water environmental function.To reach higher discharge mark
Standard, many water factories are due to design reasons, and original processing unit can not meet in existing requirement, field upgrading due to place
With the limitation of former technique, it is difficult to carry out upgrading, therefore increasing sewage treatment plant tail water depth in tale quale
Science and engineering journey has carried out planning construction.Due to using maturation process municipal sewage plant, its organic matter removal ability is stronger, goes out more
COD, BOD concentration are low in water, and relative surface water environment quality, its water outlet nitrogen, phosphorus concentration it is higher, as in advanced treating
Emphasis.
Technology in terms of existing artificial swamp is used for sewage treatment plant tail water advanced treating is more from wetland structure, leads to
The combination of different type wetland is crossed, contaminant removal efficiency is improved, but still there is artificial marsh sewage treatment system processing effect
Rate is low, and the carbon source of sewage treatment plant tail water is not enough, causes the low problem of nitric efficiency.
Utility model content
It is low that the utility model overcomes artificial marsh sewage treatment system treatment effeciency of the prior art, sewage treatment plant
The carbon source of tail water is not enough, and causing the low shortcoming of nitric efficiency, there is provided a kind of people for sewage treatment plant tail water advanced treating
Work wet land system.
The utility model realizes that the technical scheme that goal of the invention is used is:One kind is directed to sewage treatment plant tail water advanced treating
Artificial wet land system, including artificial wet land system, in addition to the ecological cell system pre-processed to sewage, described ecology
Cell system includes being provided with microbe carrier stuffing mounting bracket, microorganism in distributing channel, ecological pool and braiding channel, ecological pool pond body
Carrier filler is fixedly mounted in microbe carrier stuffing mounting bracket, and the water surface of ecological pool is plant floating bed provided with plant floating bed
Interior kind has an emergent aquactic plant one, and the water side of distributing channel and the water inlet end of ecological pool are connected, the water side of ecological pool and braiding channel
Water inlet end is connected, and being sequentially provided with lower floor from bottom of pond to pond face in the pond of artificial swamp catchments perforated pipe, rubble supporting layer, pollutant
Adsorption layer, sand filter blanket, upper strata perforation sparge pipe and emergent aquactic plant two, the water side of braiding channel and the water inlet of upper strata perforation sparge pipe
End connection, lower floor catchments perforated pipe one end provided with delivery port.
Further, described microbe carrier stuffing is non-woven fabrics.
Further, deflected current wall is provided with described ecological pool, ecological pool is separated into the pond body of plural serial stage by deflected current wall
Structure.
Further, it is described plant floating bed to be made up of one group of elemental floating body splicing.
The beneficial effects of the utility model are:Compared with Traditional Man wet land system, the utility model by ecological pool and
Being applied in combination for artificial wet land system, substantially increases sewage denitrification and dephosphorization efficiency, and nitrogen removal rate can reach more than 50%, always
Tp removal rate is up to more than 60%, and the volume loading rate of artificial swamp can be improved to 1.5m3/m2D, greatly reduces Manual moist
The floor space on ground.
Sewage of the present utility model is through distributing channel even into ecological pool, and ecological pool water inlet uses the deflector type type of flow,
Through Multi-level deflector, fully contacted with the microbe carrier stuffing in ecological pool, water inlet front end and end are due to pollutant concentration
Difference, can form different microorganism structures, and the removal to pollutant is more targeted, improves the functioning efficiency of microorganism.
Meanwhile, on the one hand the plant floating bed root system of plant of the ecological pool water surface improves contaminant removal efficiency to water body growth inside,
On the other hand, after the dry branches and fallen leaves of plant and harvesting plant regular dispensing, be that ecological pool supplements carbon source, it is ensured that anti-nitre
Being smoothed out for change effect, is converted into nitrogen by part nitrate nitrogen, realizes advanced nitrogen.The utility model such as is not aerated at the power
Equipment, carbon source uses wetland plant, greatly reduces operating cost, while reducing the expense of wetland plant outward transport disposal.
The utility model will be further described with embodiment below in conjunction with the accompanying drawings.
Brief description of the drawings
Fig. 1 is structural representation of the present utility model.
In accompanying drawing, 1 it is distributing channel, 2 is ecological pool, 3 is microbe carrier stuffing mounting bracket, 4 is that microbe carrier is filled out
Material, 5 be deflected current wall, 6 be plant floating bed, 7 be that emergent aquactic plant one, 8 is braiding channel, 9 is artificial wet land system, 10 is that lower floor catchments
Perforated pipe, 11 be rubble supporting layer, 12 be pollutant adsorption layer, 13 be sand filter blanket, 14 be emergent aquactic plant two, 15 be upper strata perforation
Sparge pipe.
Embodiment
As shown in Figure 1, a kind of artificial wet land system for sewage treatment plant tail water advanced treating of the present embodiment, bag
Artificial wet land system 9 is included, in addition to the ecological cell system pre-processed to sewage.Described ecological cell system includes distributing channel
1st, ecological pool 2 and braiding channel 8.The pond body of ecological pool 2 uses reinforced concrete structure, and pond body is square, is at least divided into two lattice of parallel connection,
Per compartment Hu Bu UNICOMs, convenient maintenance.Microbe carrier stuffing mounting bracket 3 is provided with the pond body of ecological pool 2, microbe carrier is filled out
Material 4 is fixedly mounted in microbe carrier stuffing mounting bracket 3, and the surface of microbe carrier stuffing 4 is formed on biomembrane, biomembrane
The denitrifying bacteria grown under anaerobism and anoxia condition mainly is grown in, necessary condition is provided for denitrification denitrogenation effect.This reality
The preferred microbe carrier stuffing 4 of example is applied for non-woven fabrics, thickness about 2mm, width can be pacified according to the pond body size adjusting of ecological pool 2
Dress height is no more than 3 meters, and clipping room is away from no more than 1 meter, and the filler face of microbe carrier stuffing 4 is met to inflow direction, microorganism
The rough surface of carrier filler 4, is conducive to microorganism and zooplankter apposition growth, and surface can form Tiny ecosystem structure, favorably
In the removal of pollutant.Fully contacted with microbe carrier stuffing 4 for the ease of sewage, in the preferred ecological pool 2 of the present embodiment
Provided with deflected current wall 5.Deflected current wall 5 is fixed on the lower section of ecological pool 2, the wall of deflected current wall 5 height it is high with below go out water level, deflected current wall
Opening is provided with below 5 walls, it is ensured that current are passed through.Ecological pool 2 is separated into the pond body structure of plural serial stage by deflected current wall 5, flows into
The sewage of ecological pool 2 formed in the presence of the deflected current wall 5 above and below baffling current, it is ensured that sewage and microbe carrier stuffing 4
Fully contact.The water surface of ecological pool 2 is provided with plant floating bed 6.The present embodiment is preferred plant floating bed 6 to be spliced by one group of elemental floating body
Composition.Single elemental floating body area about 3~5m2Left and right, is made up of, gross thickness about 10 protection steel plate up and down and middle foam floating body
~15cm.While ensureing to have certain buoyancy, mechanical strength is improved.It is connected between single elemental floating body using flexibility,
Because the SEA LEVEL VARIATION of ecological pool 2 is small, substantially without stormy waves.Plant floating bed 6 reserve planting holes, and empty size is:Diameter 8~
12cm, 30~50cm of spacing.Being planted in plant floating bed 6 has emergent aquactic plant 1, and emergent aquactic plant 1 includes canna, cyperus alternifolius, richness
Your bamboo etc. can hydroponics growing herbaceos perennial, root system of plant grows downwards, gos deep into pool inner water body.In Radial Oxygen Loss from Root effect
Under, root system surface forms aerobic biologic membrane, occurs nitrification, reaches the effect for removing ammonia nitrogen.The growth of plant can be from sewage
The nutriments such as middle absorption organic matter, nitrogen, phosphorus, play a part of pollutant removal.The dry branches and fallen leaves that growing process drops
And root system, carbon source is provided to water body, also can periodically be gathered in by plant, plant is periodically added to pool inner water body, forms stable
Carbon source, so as to ensure being smoothed out for denitrification, is converted into nitrogen by part nitrate nitrogen, realizes advanced nitrogen.
The water side of distributing channel 1 is connected with the water inlet end of ecological pool 2, the water side of ecological pool 2 and the water inlet end of braiding channel 8
Connection.
Described artificial swamp is downward vertical artificial wetland.It is sequentially provided with the pond of artificial swamp from bottom of pond to pond face
Lower floor catchments perforated pipe 10, rubble supporting layer 11, pollutant adsorption layer 12, sand filter blanket 13, upper strata perforation sparge pipe 15 and very water
Plant 2 14.Sand filter blanket 13, pollutant adsorption layer 12 and rubble supporting layer 11 formation packing layer gross thickness for 1.2m~
1.5m.Described lower floor catchments perforated pipe 10 for UPVC drainpipes, and caliber is not less than DN350, and open pore size is 10-15mm,
Away from 20cm, perforate direction for conduit section 1 thirty direction and 10 thirty direction, and staggeredly perforate.Rubble supporting layer 11 is main
Material is the rubble that particle diameter is 20-40mm, and thickness is 20-40mm, primarily serves support upper strata filler, and protection lower floor catchments perforation
Pipe 10, prevents upper strata from blocking the effect that pipeline collects hole compared with flour filler.The main material of pollutant adsorption layer 12 be specific surface area compared with
It is big it is broken after haydite, depth of packing is 60~80cm, and haydite process addition calcium, magnesium, aluminium, iron etc. has stronger N, P
The metallic element of adsorption capacity, is greatly improved adsorption efficiency of the system to N, P, and its particle diameter is 10-15mm, on the other hand, N, P
Adsorption layer is plant fibrous root grown layer, and the absorption of root system can also improve system organic matter and N, P removal efficiency.
The main material of sand filter blanket 13 is coarse sand, and particle diameter 0-5mm, depth of packing is 40~50cm, and clay content should be less than 10%.
Sand filter blanket 13 primarily serves interception, filtration, removes particulate matter or the biomembrane come off in the water outlet of ecological pool 2 or drops
Plant residue etc..Upper strata perforation sparge pipe 15 is UPVC drainpipes, and caliber is no more than DN100, and open pore size is 3~5mm, spacing
20cm, perforate direction for conduit section 1 thirty direction and 10 thirty direction, and staggeredly perforate.Upper strata perforation sparge pipe 15 is every
Segment pipe length less than 3m to be advisable, spacing 1.2m~2m between pipeline, and upper strata perforation sparge pipe 15 is filled out installed in sand filter blanket 13
Material top, and ensure that apopore is not blocked by coarse sand.The described prioritizing selection of emergent aquactic plant 2 14 is adapted to project location weather
The eciophyte of condition, mainly including two kinds of canna, cyperus alternifolius, iris, thaliadeabata, reed, floral leaf Lu Di, Hymenocallis americana etc. with
On herbaceos perennial.
The perforate water inlet end of sparge pipe 15 of the water side of braiding channel 8 and upper strata is connected, and lower floor one end of perforated pipe 10 of catchmenting is set
Have delivery port, the sewage after processing along lower floor catchment perforated pipe 10 water side discharge.
When actual use, comprise the following steps:
(1), sewage through distributing channel 1 to the uniform water distribution of ecological pool 2;
(2), sewage enters ecological pool 2 through step (1) uniform water distribution, and ecological pool 2 maintains anoxic or anaerobic state, dissolved oxygen
Concentration is no more than 2mg/L, is conducive to the progress of denitrification;
(3) microorganism in ecological pool 2, the synergy of plant, enter to pollutants such as the organic matter in sewage, nitrogen, phosphorus
Row processing;
(4) sewage after, being handled through step (3) enters braiding channel 8;
(5) sewage enters artificial wet land system through braiding channel 8, passes through packing layer in artificial swamp, microorganism, plant
Synergy is further handled pollutants such as the organic matter in sewage, nitrogen, phosphorus, finally, is catchmented perforated pipe by the lower floor of bottom
Discharged after 10 collections.
The present embodiment realizes denitrification denitrogenation using the Ecology Action of pretreatment system, passes through the structure of artificial wet land system
With the optimization of filler, dephosphorization efficiency is improved, realizes that effluent quality reaches《Water environment quality standard》(GB3838-2002) in
III~IV class standard.
Claims (4)
1. a kind of artificial wet land system for sewage treatment plant tail water advanced treating, including artificial wet land system, its feature exist
In in addition to the ecological cell system pre-processed to sewage, described ecological cell system includes distributing channel(1), ecological pool(2)
And braiding channel(8), ecological pool(2)Microbe carrier stuffing mounting bracket is provided with pond body(3), microbe carrier stuffing(4)Gu
Dingan County is mounted in microbe carrier stuffing mounting bracket(3)On, ecological pool(2)The water surface provided with plant floating bed(6), it is plant floating bed
(6)Interior kind has emergent aquactic plant one(7), distributing channel(1)Water side and ecological pool(2)Water inlet end connection, ecological pool(2)Go out
Water end (W.E.) and braiding channel(8)Water inlet end connection, be sequentially provided with lower floor from bottom of pond to pond face in the pond of artificial swamp and catchment perforated pipe
(10), rubble supporting layer(11), pollutant adsorption layer(12), sand filter blanket(13), upper strata perforation sparge pipe(15)And emergent aquactic plant
Two(14), braiding channel(8)Water side and upper strata perforate sparge pipe(15)Water inlet end connection, lower floor catchments perforated pipe(10)One
End is provided with delivery port.
2. a kind of artificial wet land system for sewage treatment plant tail water advanced treating according to claim 1, its feature
It is, described microbe carrier stuffing(4)For non-woven fabrics.
3. a kind of artificial wet land system for sewage treatment plant tail water advanced treating according to claim 1 or 2, it is special
Levy and be, described ecological pool(2)It is interior to be provided with deflected current wall(5), ecological pool(2)By deflected current wall(5)It is separated into the pond of plural serial stage
Body structure.
4. a kind of artificial wet land system for sewage treatment plant tail water advanced treating according to claim 1, its feature
It is, described is plant floating bed(6)It is made up of one group of elemental floating body splicing.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201720026449.4U CN206417916U (en) | 2017-01-11 | 2017-01-11 | A kind of artificial wet land system for sewage treatment plant tail water advanced treating |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201720026449.4U CN206417916U (en) | 2017-01-11 | 2017-01-11 | A kind of artificial wet land system for sewage treatment plant tail water advanced treating |
Publications (1)
Publication Number | Publication Date |
---|---|
CN206417916U true CN206417916U (en) | 2017-08-18 |
Family
ID=59574753
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201720026449.4U Active CN206417916U (en) | 2017-01-11 | 2017-01-11 | A kind of artificial wet land system for sewage treatment plant tail water advanced treating |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN206417916U (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106745777A (en) * | 2017-01-11 | 2017-05-31 | 深圳市碧园环保技术有限公司 | A kind of artificial wet land system for sewage treatment plant tail water advanced treating |
-
2017
- 2017-01-11 CN CN201720026449.4U patent/CN206417916U/en active Active
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106745777A (en) * | 2017-01-11 | 2017-05-31 | 深圳市碧园环保技术有限公司 | A kind of artificial wet land system for sewage treatment plant tail water advanced treating |
WO2018129896A1 (en) * | 2017-01-11 | 2018-07-19 | 深圳市碧园环保技术有限公司 | Artificial wetland system for advanced treatment of tail water from sewage treatment plant |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106745777A (en) | A kind of artificial wet land system for sewage treatment plant tail water advanced treating | |
CN107720973A (en) | A kind of sewage treatment plant tail water artificial wet land treating system | |
CN101905944B (en) | Composite-type sewage sludge treatment system for artificial wetland | |
CN104817239B (en) | A kind of heavily contaminated water course in situ water purification system and purification method | |
CN105461071A (en) | Green ecological floating island device | |
CN107188379A (en) | A kind of domestic sewage of villages and small towns rural area landscape type total system | |
CN105417838A (en) | High water content bidirectional flow sponge reuse system for rainwater purification and regulation and storage in wetland | |
CN107364973B (en) | Sewage treatment system, application thereof and sewage treatment method | |
CN105152487B (en) | Waters sewage-treatment plant and method | |
CN110078320A (en) | Villages and small towns sewage unpowered biological ecological treatment apparatus and the sewage disposal system comprising it | |
CN207047066U (en) | A kind of domestic sewage of villages and small towns rural area landscape type total system | |
CN109879528A (en) | Processing method and system of the domestic sewage in rural areas from driving landscape ecological | |
CN206417916U (en) | A kind of artificial wet land system for sewage treatment plant tail water advanced treating | |
CN205294963U (en) | A soil filtration system device for highway affiliated facilities sewage treatment along line | |
CN208166682U (en) | Multi-stage ecological artificial swamp for sewage disposal system | |
CN106904792A (en) | For the artificial marsh sewage treatment system in city suburbs montane park | |
CN207726821U (en) | A kind of sewage treatment plant tail water artificial wet land treating system | |
CN109879536A (en) | A kind of domestic sewage in rural areas purification system and purification method | |
CN207192930U (en) | A kind of device that black-odor riverway is administered using intensive aeration artificial swamp coupling technique dystopy | |
Li et al. | Treatment of municipal wastewater using a contact oxidation filtration separation integrated bioreactor | |
CN108751649A (en) | A kind of processing system having to rural sewage treatment excess sludge | |
CN114956354A (en) | Rural household sewage in-situ treatment system and method | |
CN101704585A (en) | Progressively reduced aeration subsurface constructed wetland | |
CN212403659U (en) | Ecological ditch for rural sewage treatment | |
CN211339184U (en) | Domestic sewage integrated treatment equipment based on steel slag ceramsite filler biological filter |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
GR01 | Patent grant | ||
GR01 | Patent grant |