CN107381976A - A kind of small watershed high-effective cleansing denitrification system and method - Google Patents
A kind of small watershed high-effective cleansing denitrification system and method Download PDFInfo
- Publication number
- CN107381976A CN107381976A CN201710839032.4A CN201710839032A CN107381976A CN 107381976 A CN107381976 A CN 107381976A CN 201710839032 A CN201710839032 A CN 201710839032A CN 107381976 A CN107381976 A CN 107381976A
- Authority
- CN
- China
- Prior art keywords
- percolation tank
- percolation
- rotating cage
- pond
- tank
- 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.)
- Withdrawn
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F2003/001—Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/009—Apparatus with independent power supply, e.g. solar cells, windpower, fuel cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2203/00—Apparatus and plants for the biological treatment of water, waste water or sewage
- C02F2203/006—Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/08—Aerobic processes using moving contact bodies
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- 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
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention discloses a kind of small watershed high-effective cleansing denitrification system and method, the system includes tidal flow artificial wetland, enhanced biological rotating cage system and modularization land percolation system, enhanced biological rotating cage system includes strengthening pond, transmission mechanism and rotating cage, rotating cage is installed on by transmission mechanism to be strengthened in pond, and matrix is filled with rotating cage;Modularization land percolation system includes continuous filter, perforation water distributor and perforated catchment pipe, continuous filter is divided into the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank by three dividing plates, perforation water distributor is installed on the top of the first percolation tank, perforated catchment pipe is installed on the bottom of continuous filter, and matrix is filled with the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank;Strengthen pond, tidal flow artificial wetland connects with hole water distributor and passes sequentially through pipeline, constant flow pump connection.The system is organically combined three, and decontamination and denitrification effect are good.This method relies on the system, simple to operation.
Description
Technical field
Environmental project technical field of sewage of the present invention, and in particular to a kind of small watershed high-effective cleansing denitrification system and side
Method.
Background technology
Restoration technique mainly includes cutting a dirt and receives the external source control technologies such as pipe, pollution of area source control, desilt and dredge etc. in
The ecological reestablishment such as source pollutant abatement technology, bank-line control, ecological purification, artificial oxygenation, and running water circulation, clear water are mended
Give, treatment in situ, bypass administer etc. other reclamation activities.Cut dirt receive pipe, face source control etc. control source cut dirty technology can be largely
Reduce pollutant and enter water body, but still suffer from and cut dirty incomplete and cause partial contamination thing to enter water body.
Marine sediments cleaning can be purified water body by the endogenous Treatment process such as desilt and dredge in a short time, but to ecology
System does great damage, and water body easily deteriorates again.The ecological reestablishments such as ecological purification, artificial oxygenation are ideal
River system repair technology, but it is limited for the effect of with serious pollution water remediation, and above-mentioned Technique on T N removal is more limited to, it is living
Water circulation, clear water supply Construction and operation are expensive.Using the treatment in situ technology of physics, chemistry or biochemical processing method, part
Chemical agent has adverse effect to water ecological environment.
Bio-carrier technology is based on biomembrance process, and target is using in the biomembrane degraded water body on bio-carrier
Pollutant, but the clean-up effect of the technology is limited by water body flow form.Those skilled in the art are more difficult expect it is how maximum
Play to limit the degradation that bio-carrier removes pollutant, while in the prior art, water plant and microbes with
Water body is lost in, and causes unstable to river water body regulation effect.
To sum up, in the case of cutting dirt in control source, only integrate and improve existing ecological reestablishment, and incorporate microorganism remediation
Technology, water pollution problem could really be solved by carrying out integrated, systematization to technology.But how prior art to be carried out
It is efficiently modified and reasonably integrates, realizes the sustainable reparation of water body, turn into urgent problem to be solved.
The content of the invention
In order to solve the above-mentioned problems of the prior art, the invention provides a kind of small watershed high-effective cleansing denitrification system
And method, the system are organically combined biological rotary cage system, tidal flow artificial wetland and modularization land percolation system,
It is high to handle load, decontamination and denitrification effect are good.
The decontamination denitrogenation method relies on said system, simple to operation, can continuously run, and decontamination and denitrification effect are good.
Technical scheme is used by realizing above-mentioned purpose of the present invention:
A kind of small watershed high-effective cleansing denitrification system, including electric power system and tidal flow artificial wetland, tidal flow artificial are wet
Tide matrix, in addition to enhanced biological rotating cage system and modularization land percolation system, enhanced biological rotating cage system are filled with ground
System includes transmission mechanism and rotating cage, and rotating cage is installed on cross section of river by transmission mechanism;Or enhanced biological rotating cage system bag
Include and strengthen pond, transmission mechanism and rotating cage, rotating cage is installed on by transmission mechanism to be strengthened in pond, filled with reinforcing matrix in rotating cage;
Modularization land percolation system includes continuous filter, perforation water distributor and perforated catchment pipe, continuous filter interior edge continuous filter
Length direction is provided with first partition, second partition and the 3rd dividing plate, and first partition, second partition and the 3rd dividing plate are each perpendicular to ooze
Filter tank bottom, the height of first partition, second partition and the 3rd dividing plate are sequentially reduced along the direction for being percolated pond length, continuous filter quilt
First partition, second partition and the 3rd dividing plate are divided into the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank,
The bottom of first percolation tank and the second percolation tank connects, and the bottom of the second percolation tank, the 3rd percolation tank and the 4th percolation tank is successively
Separate, be sequentially communicated at the top of the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank, perforation water distributor peace
Top loaded on the first percolation tank, perforated catchment pipe are installed on the bottom of continuous filter, and perforated catchment pipe is through the first percolation tank, the
The bottom of two percolation tanks, the 3rd percolation tank and the 4th percolation tank, the first percolation tank is interior to be filled with the first filtration matrices, the second diafiltration
The second filtration matrices are filled with groove, the 3rd filtration matrices are filled with the 3rd percolation tank, the 4th is filled with the 4th percolation tank
Filtration matrices;
The outlet for strengthening pond is connected by pipeline, the first timing constant flow pump with the entrance of tidal flow artificial wetland, tidal current
The outlet of artificial swamp is connected by pipeline, the second timing constant flow pump with perforation water distributor.
Described transmission mechanism includes motor and rotating shaft, and motor is installed on bank, and the both ends of rotating shaft are installed by bearing
In two on the bank, the output axis connection that one end of rotating shaft passes through shaft coupling and motor;Or motor is installed on and strengthened outside pond, rotating shaft
One end is installed on the center for strengthening the side wall of pond one by bearing, and the other end of rotating shaft passes through the center for strengthening another opposing sidewalls in pond
And be installed on and strengthened in the side wall of pond by bearing, the output axis connection that the other end of rotating shaft passes through shaft coupling and motor;Rotating shaft
It is interspersed in rotating cage, rotating cage is fixed in rotating shaft.
Described reinforcing matrix is carbon fibre ball, a diameter of 5-8cm of carbon fibre ball, and the volume of carbon fibre ball is
The 3/4 of rotating cage volume.
Rotating cage cage is provided with artificial aquatic weed on the net.
First filtration matrices are followed successively by soil horizon, fine sand layer, the first granule rock layers and cobble rock layers from top to bottom, and second oozes
Filter matrix is followed successively by soil horizon, turf layer, permeable geotextile layer, the first granule rock layers and cobble rock layers from top to bottom, and the 3rd oozes
Filter matrix is followed successively by soil horizon, turf layer, the first granule rock layers and cobble rock layers from top to bottom, and the 4th filtration matrices are from top to bottom
Soil horizon, turf layer, permeable geotextile layer, the first granule rock layers and cobble rock layers are followed successively by, perforation water distributor oozes positioned at first
Between soil horizon and the fine sand layer of filtering matrix, the bottom of first partition is located in the cobble rock layers of the first filtration matrices, perforation collection
Water pipe is located in the coarse gravel of the first filtration matrices, the second filtration matrices, the 3rd filtration matrices and the 4th filtration matrices, and second oozes
The soil horizon bottom of matrix, the 3rd filtration matrices and the 4th filtration matrices is filtered with being flushed at the top of the 3rd dividing plate, the first diafiltration base
The soil horizon bottom of matter at the top of first partition with flushing.
Cobble rock layers, the first granule rock layers, turf layer have been sequentially filled in described tidal flow artificial wetland from bottom to up
With the second granule rock layers, the particle diameter of the first bird's-eye gravel is less than the particle diameter of the second bird's-eye gravel, and tidal flow artificial wetland is interior thin second
Plantation has emergent aquactic plant on gravel layer.
The pipeline that the outlet of tidal flow artificial wetland connects with perforation water distributor is provided with industrial flow meter, industrial flow meter
Between the second timing constant flow pump and perforation water distributor, the exit of perforated catchment pipe is provided with time control solenoid valve.
Described electric power system includes solar panel, and electric power system is that motor, the first timing constant flow pump and second are fixed
When constant flow pump power.
Compared with prior art, advantages of the present invention is with beneficial effect:
1st, the motor in enhanced biological rotating cage system is generated electricity by solar panel and driven, and energy consumption cost is low, while rotating cage
Play that aeration is carried out to water body is micro- with strengthening during rotation (can intelligent automatic regulated rotating speed, accelerate the biofilm of matrix)
The effect of the detergent power of biology, and its surface of rotating cage is provided with artificial aquatic weed, and inside is filled with carbon fibre ball, not only strengthened
Indigenous microorganism accumulation ability, while carbon source is also provided, enhance water body purification ability.
2nd, it (can enter in river that the reinforcing pond of enhanced biological rotating cage system can be built in small rivers section
Row in-situ immobilization) or structures pond body, can carry out in situ or showering, rotating cage according to Environmental Status can be according to reinforcing
Pond size carries out multiple serial or parallel connection splicings, has application flexible, and energy consumption is low, the advantages that high treating effect.
3rd, tidal flow artificial wetland can alleviate tidal current wetland and aftertreatment systems block up from while carbon source is provided
The problems such as plug, at the same the mode of operation of tidal current can oxygen-enriched effect in consolidation system, further enhance oxidation Decomposition and nitre
Change acts on.
4th, modularization land percolation internal system sets first partition, second partition, the 3rd dividing plate, and continuous filter is divided successively
For the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank, the anti-impact of hydraulic detention time and system is added
Load-bearing capacity is hit, ensure that the anaerobic environment of whole system, turf provides carbon source, makes denitrification efficiency higher, so as to which denitrogenation is imitated
Fruit is more preferable, and dividing plate elevation reduces successively, ensures that each percolation tank is smoothly intake water outlet, while in the second, the 4th filtration system
The problems such as portion sets 3-5cm permeable geotextiles, and further enriched microorganism and relieving system block.
5th, tidal flow artificial wetland and modularization land percolation system use periodic running mode, both full of when
Between with drain time be exactly in interleaved state, so as to ensure that whole system is continuously run.
The bright book of accompanying drawing
Fig. 1 is the structural representation of the small watershed high-effective cleansing denitrification system of the present invention.
Wherein, 1- strengthens pond, 2- motors, 3- rotating shafts, 4- rotating cages, 5- artificial aquatic weeds, 6- carbon fibres ball, the timings of 7- first
Constant flow pump, 8- emergent aquactic plants, 9- turfs layer, 10- tidal flow artificial wetlands, 11- cobbles rock layers, the first granules of 12- rock layers, 13-
Second granule rock layers, the second timings of 14- constant flow pump, 15- industrial flows meter, 16- first partitions, 17- fine sand layers;18- continuous filters;
19- perforation water distributors;20- second partitions;The dividing plates of 21- the 3rd, 22- perforated catchment pipes, the permeable geotextiles of 23-;24- soil horizons,
25- time control solenoid valves, the percolation tanks of 26- first, the percolation tanks of 27- second, the percolation tanks of 28- the 3rd, the percolation tanks of 29- the 4th, 30-
Solar panel.
Embodiment
The small watershed high-effective cleansing denitrification system of the present invention is described in detail below in conjunction with the accompanying drawings.
The structure of small watershed high-effective cleansing denitrification system provided by the invention as shown in figure 1, the system include electric power system,
Tidal flow artificial wetland 10, enhanced biological rotating cage system and modularization land percolation system.
Enhanced biological rotating cage system includes transmission mechanism and rotating cage 4, and transmission mechanism includes motor 2 and rotating shaft 3.Rotating cage 4 can
To be located on cross section of river, two are installed on the bank by rotating shaft 3, motor is installed on bank, can thus be carried out in river former
Repair position;Or construct strengthen the progress of pond 1 showering in addition, motor 2, which is installed on, to be strengthened outside pond 1, and one end of rotating shaft 3 passes through axle
The center for being installed on and strengthening the side wall of pond 1 one is held, the other end of rotating shaft 3 through the center for strengthening 1 another opposing sidewalls of pond and passes through
Bearing, which is installed on, to be strengthened in the side wall of pond 1, and the other end of rotating shaft 3 passes through the output axis connection of shaft coupling and motor 2.Rotating shaft 3 is worn
It is inserted in rotating cage 4, rotating cage 4 is fixed in rotating shaft 3.Rotating cage long 1.5-2m, diameter 50cm, can the splicing of multiple serial or parallel connections, turn
The rotating speed of cage can carry out Intelligent adjustment by motor.Carbon fibre ball 6, a diameter of 5- of carbon fibre ball 6 are filled with rotating cage 4
8cm, the volume of carbon fibre ball 6 are the 3/4 of the volume of rotating cage 4.The cage of rotating cage 4 is provided with artificial aquatic weed 5 on the net, and artificial aquatic weed is mainly
Material cheap and easy to get and larger specific surface area is made, for example, bar shaped non-woven fabrics.
Cobble rock layers 11, the first granule rock layers 12, turf layer 9 have been sequentially filled in tidal flow artificial wetland 10 from bottom to up
With the second granule rock layers 13.Plantation has emergent aquactic plant 8 in the second granule rock layers in tidal flow artificial wetland 10, and emergent aquactic plant is
Emergent aquactic plant with local advantage.The particle diameter of first bird's-eye gravel is 8-16mm, and filling thickness 30cm, turf is by permeable geotechnique
Cloth wraps up, filling thickness 10cm, and the particle diameter of the second bird's-eye gravel is 4-8mm, filling thickness 30cm, and the particle diameter of coarse gravel is
16-32mm, filling thickness 20cm.
Modularization land percolation system includes continuous filter 18, perforation water distributor 19 and perforated catchment pipe 22.In continuous filter 18
First partition 16, the dividing plate 21 of second partition 20 and the 3rd, first partition 16, the and of second partition 20 are provided with along continuous filter length direction
3rd dividing plate 21 is each perpendicular to the bottom of continuous filter 18, first partition 16, the diafiltration of the height of the dividing plate 21 of second partition 20 and the 3rd edge
The direction of pond length is sequentially reduced.Continuous filter 18 is divided for the first diafiltration by first partition 16, the dividing plate 21 of second partition 20 and the 3rd
The bottom of groove 26, the second percolation tank 27, the 3rd percolation tank 28 and the 4th percolation tank 29, the first percolation tank 26 and the second percolation tank 27
Connection, the bottom of the second percolation tank 27, the 3rd percolation tank 28 and the 4th percolation tank 29 separate successively, the first percolation tank 26, second
The top of percolation tank 27, the 3rd percolation tank 28 and the 4th percolation tank 29 is sequentially communicated.In first percolation tank 26 from top to bottom successively
Filled with soil horizon 24 (filling thickness 10cm), fine sand layer 17 (filling thickness 15cm), (filling is thick for the first granule rock layers 12
Spend for 30cm) and cobble rock layers 11 (filling thickness 20cm), soil horizon has been sequentially filled from top to bottom in the second percolation tank 27
24 (filling thickness 15cm), turf layer 9 (filling thickness 10cm), permeable geotextile layer 23 (thickness 5cm), the first granule
Rock layers 12 (thickness 25cm) and cobble rock layers 11 (filling thickness 20cm), it has been sequentially filled from top to bottom in the 3rd percolation tank 28
(filling thickness is for soil horizon 24 (filling thickness 15cm), turf layer 9 (filling thickness 10cm), the first granule rock layers 12
30cm) and cobble rock layers 11 (filling thickness 20cm), soil horizon 24 has been sequentially filled from top to bottom in the 4th percolation tank 29 (to fill out
It is 15cm to fill thickness), turf layer 9 (filling thickness 10cm), permeable geotextile layer 23 (filling thickness 5cm), the first granule
Rock layers 12 (thickness 25cm) and cobble rock layers 11 (filling thickness 20cm).Second percolation tank 27, the 3rd percolation tank 28 and the 4th
Soil horizon bottom in percolation tank 29 flushes with the top of the 3rd dividing plate 21, the soil horizon bottom and first in the first percolation tank 26
The top of dividing plate 16 flushes.Perforation water distributor 19 is located between the soil horizon 24 in the first percolation tank 26 and fine sand layer 17, and first
The bottom of dividing plate 16 is located in the cobble rock layers 11 in the first percolation tank 26, and perforated catchment pipe 22 is located at the first percolation tank 26,
In cobble rock layers 11 in two percolation tanks 27, the 3rd percolation tank 28 and the 4th percolation tank 29.The exit of perforated catchment pipe 22 is set
Having time controls magnetic valve 25, and time control solenoid valve 25 is the magnetic valve with the time relay.
The outlet for strengthening pond 1 is connected by pipeline, the first timing constant flow pump 7 with the entrance of tidal flow artificial wetland 10, tide
The outlet of nighttide artificial wetland 10 is connected by pipeline, the second timing constant flow pump 14 and industrial flow meter 15 and perforation water distributor 19
Logical, industrial flow meter 15 is located between the second timing constant flow pump 14 and perforation water distributor 19.First timing constant flow pump and the second perseverance
It is the flow pump with the time relay to flow pump.Industrial flow meter is by setting uninterrupted, to control into modularization soil
The hydraulic load of filtration system, while for measuring the relevant parameter of flow, determine whether the system is run in normal scope,
There is deficiency or more than relevant parameter, flow will be adjusted, so as to ensure the normal work of system.
Described electric power system includes solar panel 30, motor 2, the first timing constant flow pump 7, the second timing constant flow pump
14 and time control solenoid valve 25 by solar panel generate electricity drive, solar power generation energy-saving environmental protection, save denitrogenation cost.
Small watershed high-effective cleansing denitrogenation method with reference to above-mentioned small watershed high-effective cleansing denitrification system to the present invention
It is described in detail.
The method that decontamination denitrogenation is carried out based on above-mentioned small watershed high-effective cleansing denitrification system is as follows:
If the 1, rotating cage is installed on cross section of river and carries out in-situ immobilization, sewage is directly over rotating cage, if constructing in addition
To strengthen pond and carry out showering, then sewage is pumped into and strengthened in pond, hydraulic detention time 3-12h, motor driving rotating cage rotates,
Artificial aquatic weed and the indigenous microorganism of carbon fibre ball enrichment carry out aerobic decomposition and nitrification, obtain one-level sewage;
2nd, one-level sewage is pumped into tidal flow artificial wetland by very first time constant flow pump, passes through very first time constant flow pump
Control the flooding time of tidal flow artificial wetland, flooding time 10-30min, the hydraulic detention time of tidal flow artificial wetland
For 3-12h (according to the cycle of operation determined, calculating the residence time after tidal flow artificial wetland is full of and drained), one-level
Organic pollution in sewage is attached to biomembrane absorption and oxidation Decomposition in tide matrix, ammonia nitrogen (NH3- N) it is oxidized
Into nitrate nitrogen and nitrite nitrogen (NO3-N、NO2- N), the adsorbed retention of phosphorus, while carry out ion exchange and anti-nitration reaction, one-level
Mass fraction is that 0.6-17.3% nitrogen and 1.4-41.2% phosphorus are absorbed by emergent aquactic plant in sewage, obtains B-grade sewage;
3rd, B-grade sewage is pumped into continuous filter by the second time constant flow pump, and by perforating, water distributor enters the first continuous filter,
B-grade sewage passes sequentially through the first continuous filter, the second continuous filter, the 3rd continuous filter and the 4th continuous filter, persistently carries out aerobic point
Solution, nitration reaction and anti-nitration reaction (carbon source needed for anti-nitration reaction is provided by turf), go removal organic polluter, total nitrogen and
Total phosphorus, obtain three-level sewage.
4th, three-level sewage is drained through time control solenoid valve, the drain time and tidal current of modularization land percolation system
The filling time of artificial swamp is identical.The drain time of modularization land percolation system and the filling time of tidal flow artificial wetland
Interleaved state is exactly in, tidal flow artificial wetland is used periodic running mode with improving modularization land percolation system
(intermittent time 3-12h), two systems interleaved operation, so as to ensure that whole system is carried out continuously.
One section of pollution small river in southern somewhere, is handled using above-mentioned small watershed high-effective cleansing denitrification system and method
Polluted river water, the sewage quality situation of the small river are as follows:COD concentration is 200mg/L (170-240mg/L), NH3- N concentration is
8mg/L (7-10mg/L), TN concentration are 10mg/L (9-13mg/L), TP concentration is 1mg/L (0.8-1.3mg/L), pH 6-7,
28 DEG C of water temperature.It is 12h in the intermittent duty cycle, the water outlet to system water outlet is sampled detection, the water quality situation of water outlet
It is as follows:COD concentration is 28.8mg/L (clearance 85.6%), NH3- N concentration is 1.17mg/L (clearance 85.4%),
TN concentration is 1.8mg/L (clearance 82%), and TP concentration is 0.099mg/L (clearance 90.1%).Effluent quality index,
Reach four class water above standards in water environment quality standard (GB 3838-2002) on the whole.
Claims (9)
1. a kind of small watershed high-effective cleansing denitrification system, including electric power system and tidal flow artificial wetland, tidal flow artificial wetland
It is interior to be filled with tide matrix, it is characterised in that:Also include enhanced biological rotating cage system and modularization land percolation system, strengthen life
Thing rotating cage system includes transmission mechanism and rotating cage, and rotating cage is installed on cross section of river by transmission mechanism;Or enhanced biological turns
Cage system includes strengthening pond, transmission mechanism and rotating cage, and rotating cage is installed on by transmission mechanism to be strengthened in pond, filled with strong in rotating cage
Change matrix;
Modularization land percolation system includes continuous filter, perforation water distributor and perforated catchment pipe, continuous filter interior edge diafiltration pond length
Direction is provided with first partition, second partition and the 3rd dividing plate, and first partition, second partition and the 3rd dividing plate are each perpendicular to continuous filter
Bottom, the height of first partition, second partition and the 3rd dividing plate are sequentially reduced along the direction for being percolated pond length, and continuous filter is by first
Dividing plate, second partition and the 3rd dividing plate are divided into the first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank, and first
The bottom of percolation tank and the second percolation tank connects, and the bottom of the second percolation tank, the 3rd percolation tank and the 4th percolation tank separates successively,
It is sequentially communicated at the top of first percolation tank, the second percolation tank, the 3rd percolation tank and the 4th percolation tank, perforation water distributor is installed on the
The top of one percolation tank, perforated catchment pipe are installed on the bottom of continuous filter, and perforated catchment pipe is percolated through the first percolation tank, second
The bottom of groove, the 3rd percolation tank and the 4th percolation tank, the first percolation tank is interior to be filled with the first filtration matrices, is filled out in the second percolation tank
Filled with the second filtration matrices, the 3rd filtration matrices are filled with the 3rd percolation tank, the 4th diafiltration base is filled with the 4th percolation tank
Matter;
The outlet for strengthening pond is connected by pipeline, the first timing constant flow pump with the entrance of tidal flow artificial wetland, tidal flow artificial
The outlet of wetland is connected by pipeline, the second timing constant flow pump with perforation water distributor.
2. small watershed high-effective cleansing denitrification system according to claim 1, it is characterised in that:Described transmission mechanism includes
Motor and rotating shaft, motor are installed on bank, and the both ends of rotating shaft are installed on two on the bank by bearing, and one end of rotating shaft passes through shaft coupling
The output axis connection of device and motor;Or motor is installed on and strengthened outside pond, one end of rotating shaft is installed on by bearing strengthens pond one
The center of side wall, the other end of rotating shaft are installed on reinforcing pond side through the center for strengthening another opposing sidewalls in pond and by bearing
On wall, output axis connection that the other end of rotating shaft passes through shaft coupling and motor;Rotating shaft is interspersed in rotating cage, and rotating cage is fixed on rotating shaft
On.
3. small watershed high-effective cleansing denitrification system according to claim 2, it is characterised in that:Described reinforcing matrix is carbon
Cellulose fiber ball, a diameter of 5-8cm of carbon fibre ball, the volume of carbon fibre ball are the 3/4 of rotating cage volume.
4. small watershed high-effective cleansing denitrification system according to claim 3, it is characterised in that:Rotating cage cage is provided with artificial on the net
Pasture and water.
5. small watershed high-effective cleansing denitrification system according to claim 2, it is characterised in that:First filtration matrices are from up to
Under be followed successively by soil horizon, fine sand layer, the first granule rock layers and cobble rock layers, the second filtration matrices and be followed successively by soil from top to bottom
Layer, turf layer, permeable geotextile layer, the first granule rock layers and cobble rock layers, the 3rd filtration matrices are followed successively by soil from top to bottom
Layer, turf layer, the first granule rock layers and cobble rock layers, the 4th filtration matrices are followed successively by soil horizon, turf layer, permeable from top to bottom
Geotextile layer, the first granule rock layers and cobble rock layers, perforation water distributor be located at the first filtration matrices soil horizon and fine sand layer it
Between, the bottom of first partition is located in the cobble rock layers of the first filtration matrices, and perforated catchment pipe is located at the first filtration matrices, second
In the coarse gravel of filtration matrices, the 3rd filtration matrices and the 4th filtration matrices, the second filtration matrices, the 3rd filtration matrices and the 4th
The soil horizon bottom of filtration matrices with being flushed at the top of the 3rd dividing plate, the soil horizon bottoms of the first filtration matrices and first partition
Top flushes.
6. small watershed high-effective cleansing denitrification system according to claim 2, it is characterised in that:Described tide matrix is under
Supreme to be followed successively by cobble rock layers, the first granule rock layers, turf layer and the second granule rock layers, the particle diameter of the first bird's-eye gravel is less than second
The particle diameter of bird's-eye gravel, the interior plantation in the second granule rock layers of tidal flow artificial wetland have emergent aquactic plant.
7. small watershed high-effective cleansing denitrification system according to claim 2, it is characterised in that:Tidal flow artificial wetland goes out
Mouth is provided with industrial flow meter with the pipeline that perforation water distributor connects, and industrial flow meter is located at the second timing constant flow pump and perforation cloth
Between water pipe, the exit of perforated catchment pipe is provided with time control solenoid valve.
8. small watershed high-effective cleansing denitrification system according to claim 2, it is characterised in that:Described electric power system includes
Solar panel, electric power system are motor, the first timing constant flow pump and the power supply of the second timing constant flow pump.
9. a kind of method that decontamination denitrogenation is carried out based on any described small watershed high-effective cleansing denitrification systems of claim 1-8,
Comprise the following steps:
If the 9.1, rotating cage is installed on cross section of river and carries out in-situ immobilization, sewage is directly over rotating cage, if constructing in addition strong
Change pond and carry out showering, then sewage is pumped into and strengthened in pond, hydraulic detention time 3-12h, motor driving rotating cage rotates, people
The indigenous microorganism of work pasture and water and the enrichment of carbon fibre ball carries out aerobic decomposition and nitrification, obtains one-level sewage;
9.2nd, one-level sewage is pumped into tidal flow artificial wetland by very first time constant flow pump, passes through very first time constant flow pump control
The flooding time of tidal flow artificial wetland processed, flooding time 10-30min, the hydraulic detention time of tidal flow artificial wetland are
3-12h, the organic pollution in one-level sewage is attached to biomembrane absorption in tide matrix and oxidation Decomposition, ammonia nitrogen are damp
Nighttide matrix is oxidized to nitrate nitrogen and nitrite nitrogen, the adsorbed retention of phosphorus, while carries out ion exchange and anti-nitration reaction, and one-level is dirty
Mass fraction is that 0.6-17.3% nitrogen and 1.4-41.2% phosphorus are absorbed by emergent aquactic plant in water, obtains B-grade sewage;
9.3rd, B-grade sewage is pumped into continuous filter by the second time constant flow pump, enters the first continuous filter by water distributor of perforating, and two
Level sewage pass sequentially through the first continuous filter, the second continuous filter, the 3rd continuous filter and the 4th continuous filter, persistently carry out it is aerobic decompose,
Nitration reaction and anti-nitration reaction, removal organic polluter, total nitrogen and total phosphorus are removed, obtain three-level sewage.
9.4th, three-level sewage is drained through time control solenoid valve, drain time and the tide person who lives in exile of modularization land percolation system
The filling time of work wetland is identical.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710839032.4A CN107381976A (en) | 2017-09-18 | 2017-09-18 | A kind of small watershed high-effective cleansing denitrification system and method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710839032.4A CN107381976A (en) | 2017-09-18 | 2017-09-18 | A kind of small watershed high-effective cleansing denitrification system and method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107381976A true CN107381976A (en) | 2017-11-24 |
Family
ID=60350267
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710839032.4A Withdrawn CN107381976A (en) | 2017-09-18 | 2017-09-18 | A kind of small watershed high-effective cleansing denitrification system and method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107381976A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110980966A (en) * | 2019-12-18 | 2020-04-10 | 南京公诚节能新材料研究院有限公司 | Combined artificial aquatic weed |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006150351A (en) * | 2004-11-05 | 2006-06-15 | Kato Construction Co Ltd | Wetland type water purification system |
KR100874503B1 (en) * | 2007-08-24 | 2008-12-18 | 주식회사 에코탑 | Constructed wetland structure for sewage treatment |
CN104150691A (en) * | 2014-07-25 | 2014-11-19 | 中国环境科学研究院 | Composite alternate flow wetland molecular sieve biological rotating disc treatment system and method |
CN104150693A (en) * | 2014-07-25 | 2014-11-19 | 中国环境科学研究院 | Advanced turbid sewage treatment device and method for multi-segmental composite vertical flow soil infiltration device |
CN104150715A (en) * | 2014-08-20 | 2014-11-19 | 中国环境科学研究院 | Sewage treatment device by combining tidal current artificial marsh and soil percolation system and method thereof |
CN105152467A (en) * | 2015-08-11 | 2015-12-16 | 华中农业大学 | Intensive deep decontamination and denitrification treatment system and method for domestic sewage |
-
2017
- 2017-09-18 CN CN201710839032.4A patent/CN107381976A/en not_active Withdrawn
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006150351A (en) * | 2004-11-05 | 2006-06-15 | Kato Construction Co Ltd | Wetland type water purification system |
KR100874503B1 (en) * | 2007-08-24 | 2008-12-18 | 주식회사 에코탑 | Constructed wetland structure for sewage treatment |
CN104150691A (en) * | 2014-07-25 | 2014-11-19 | 中国环境科学研究院 | Composite alternate flow wetland molecular sieve biological rotating disc treatment system and method |
CN104150693A (en) * | 2014-07-25 | 2014-11-19 | 中国环境科学研究院 | Advanced turbid sewage treatment device and method for multi-segmental composite vertical flow soil infiltration device |
CN104150715A (en) * | 2014-08-20 | 2014-11-19 | 中国环境科学研究院 | Sewage treatment device by combining tidal current artificial marsh and soil percolation system and method thereof |
CN105152467A (en) * | 2015-08-11 | 2015-12-16 | 华中农业大学 | Intensive deep decontamination and denitrification treatment system and method for domestic sewage |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110980966A (en) * | 2019-12-18 | 2020-04-10 | 南京公诚节能新材料研究院有限公司 | Combined artificial aquatic weed |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101163061B1 (en) | Equipment and method for water and stream purification using layered soil system | |
CN103332789B (en) | Method for ecologically purifying black and odorous riverway water body | |
CN101723520B (en) | Method for cutting low-pollution water load of venous riverway | |
CN101898856B (en) | Subsurface flow constructed wetland system of secondary effluent from sewage treatment plant and application thereof | |
CN102190376B (en) | Integrated flow constructed wetland treatment system | |
CN102464404B (en) | Method and system for remediation and treatment of polluted river water | |
CN102557330A (en) | An/O type composite artificial wetland system for enhanced treatment of low-C/N ratio wastewater | |
US20150101981A1 (en) | Assemblies and methods for treating wastewater | |
CN110550829A (en) | Tower type ecological purification integrated device for domestic sewage of small towns | |
CN109607975B (en) | Constructed wetland structure for repairing super-eutrophic water body and endogenous pollution | |
CN207451863U (en) | A kind of modularization is layered bio-trickling sewage disposal system | |
CN102838208A (en) | River channel purifier technology for polluted river water quality improvement | |
CN109626760A (en) | Rain dirt mixed flow drains total system and method | |
CN107381976A (en) | A kind of small watershed high-effective cleansing denitrification system and method | |
CN2887857Y (en) | Submerged bio-membrane and active sludge composite bio-treatment system | |
CN103601291B (en) | A kind of method for the treatment of low carbon-nitrogen ratio sewage and denitrification filtration system | |
CN213924419U (en) | Contain salt domestic sewage treatment plant | |
CN108128885A (en) | Eliminate the river channel ecology processing system of tidal waterway black and odorous water | |
CN104556532A (en) | Artificial wetland purifying system | |
Borkar et al. | Tidal flow constructed wetland: An overview | |
CN209583913U (en) | Rain dirt mixed flow drain treatment apparatus | |
CN102897976B (en) | Method for in-situ ecological treatment of town domestic waste water by using river and creek converging | |
CN207294513U (en) | A kind of sewage plant tail water peer is discharged into processing system | |
JPH06312196A (en) | Water purifying apparatus for rivers | |
CN111943434A (en) | Micro-polluted drinking water source biological ecological restoration system and method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
WW01 | Invention patent application withdrawn after publication | ||
WW01 | Invention patent application withdrawn after publication |
Application publication date: 20171124 |