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 PDF

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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
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China
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percolation tank
percolation
rotating cage
pond
tank
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CN201710839032.4A
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Chinese (zh)
Inventor
肖林
王昕�
崔红军
王龙涛
洪军
匡丕桩
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Gezhouba Dam Luyuan Group China Technology Co Ltd
Gezhouba China Technology Co Ltd
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Gezhouba Dam Luyuan Group China Technology Co Ltd
Gezhouba China Technology Co Ltd
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Priority to CN201710839032.4A priority Critical patent/CN107381976A/en
Publication of CN107381976A publication Critical patent/CN107381976A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F2003/001Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/009Apparatus with independent power supply, e.g. solar cells, windpower, fuel cells
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/08Aerobic processes using moving contact bodies
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • 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

A kind of small watershed high-effective cleansing denitrification system and method
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.
CN201710839032.4A 2017-09-18 2017-09-18 A kind of small watershed high-effective cleansing denitrification system and method Withdrawn CN107381976A (en)

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