CN111635065A - Ecological bank protection clean system - Google Patents

Ecological bank protection clean system Download PDF

Info

Publication number
CN111635065A
CN111635065A CN202010366066.8A CN202010366066A CN111635065A CN 111635065 A CN111635065 A CN 111635065A CN 202010366066 A CN202010366066 A CN 202010366066A CN 111635065 A CN111635065 A CN 111635065A
Authority
CN
China
Prior art keywords
layer
water
bank protection
purification system
ecological bank
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.)
Pending
Application number
CN202010366066.8A
Other languages
Chinese (zh)
Inventor
赵化祥
陈勇
郭强
任晓彬
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Dongguan Dianjian Water Environment Treatment Technology Co ltd
Original Assignee
Dongguan Dianjian Water Environment Treatment Technology Co ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Dongguan Dianjian Water Environment Treatment Technology Co ltd filed Critical Dongguan Dianjian Water Environment Treatment Technology Co ltd
Priority to CN202010366066.8A priority Critical patent/CN111635065A/en
Publication of CN111635065A publication Critical patent/CN111635065A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/2806Anaerobic processes using solid supports for microorganisms
    • 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
    • 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
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used

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)
  • Treatment Of Biological Wastes In General (AREA)

Abstract

The invention provides an ecological bank protection purification system, which belongs to the technical field of ecological bank protection and comprises the following components: a plurality of water-proof cavities, a flow guide pipe, a water absorption layer, a microbial degradation layer and a soil layer. A plurality of water proof cavity are used for placing in the foundation ditch of river course bank slope, and it has adsorbed layer, eluviation layer and denitrification layer to fill in proper order in the three reaction tank that from top to bottom arranges. The bottom of the water absorption layer is connected with a first water diversion layer and a second water diversion layer; the first water diversion layer is used for guiding liquid in a river channel, and the second water diversion layer is used for guiding liquid in a water outlet. The microbial degradation layer is laid on the water absorption layer. The soil layer is laid on the microbial degradation layer and used for planting plants. The ecological bank protection purification system provided by the invention can decompose organic matters into inorganic matters and provide nutrients for the soil layer above the ecological bank protection purification system through biodegradation, and liquid in the water absorption layer continuously moves upwards without external force so as to carry the nutrients to supply plants, thereby ensuring the normal operation of the whole system.

Description

Ecological bank protection clean system
Technical Field
The invention belongs to the technical field of ecological bank protection, and particularly relates to an ecological bank protection purification system.
Background
In recent years, the ecological environment of the river is seriously damaged, and the phenomena of eutrophication and water and soil loss frequently occur. Therefore, effective control of pollutants entering water bodies of rivers and lakes and prevention of large-area water and soil loss become important importance in river ecological environment treatment.
The existing river channel treatment bank protection technology mainly comprises the following types: natural bank protection, hard bank protection, ecological bank protection and the like. The natural revetment is a revetment which is formed by planting plants on a river revetment, and is used for fixing soil and preventing sand and effectively intercepting nitrogen and phosphorus of runoff by utilizing developed root systems of the plants, but the revetment is poor in stability and is easy to erode and destroy in an area with sufficient rainwater; the hard revetment is a structure mainly composed of stones or concrete, and the revetment has great harm to a river ecosystem, blocks the connection between the river ecosystem and a land ecosystem and seriously influences the biological diversity; at present, the ecological bank protection technology is generally adopted, and the method specifically comprises the following modes: the ecological concrete revetment, the hinge type revetment, the ecological bag type revetment and the like have certain effects on the interception of pollutants and the protection of the revetment, and the landscape of the revetment is improved to a certain extent. However, the existing ecological revetment can only reduce the content of specific elements in sewage, organic matters in the sewage cannot be degraded, and the existing ecological revetment directly introduces the sewage into a river channel or permeates the underground after the sewage is treated, so that inorganic matters and the like in the treated sewage are not supplied to plants on the ecological revetment as nutrients, thereby not only damaging the environment, but also wasting resources.
Disclosure of Invention
The invention aims to provide an ecological bank protection purification system, and aims to solve the problems that inorganic matters and the like in treated sewage are not supplied to plants on an ecological bank protection as nutrients due to the fact that the treated sewage is directly introduced into a river channel or permeates into the ground, the environment is damaged, and resources are wasted.
In order to achieve the purpose, the invention adopts the technical scheme that: providing an ecological bank protection purification system comprising:
the water-proof cavities are used for being placed in foundation pits of a river bank slope and are arranged along the length direction of the river; the top and the bottom of the waterproof cavity are respectively provided with a water inlet and a water outlet; two superfine fiber layers are sequentially arranged along the length direction of the waterproof cavity; the two superfine fiber layers and the water-proof cavity are enclosed into three reaction tanks, and an adsorption layer, a leaching layer and a denitrification layer are sequentially filled in the three reaction tanks which are arranged from top to bottom;
the drainage pipe is positioned at the tops of the water-proof cavities and used for conveying sewage to the water-proof cavities, and a plurality of floating balls used for opening and closing the water inlets are mounted on the drainage pipe;
the water absorption layer is laid on the side face, far away from the foundation pit, of the water-resisting cavity, the bottom of the water absorption layer is connected with a first water diversion layer and a second water diversion layer, the first water diversion layer is used for guiding liquid of the river channel, and the second water diversion layer is used for guiding liquid of the water outlet;
the microbial degradation layer is laid on the water absorption layer and is used for performing biodegradation on liquid flowing in from the water absorption layer; and
and the soil layer is laid on the microbial degradation layer and is used for planting plants.
As another embodiment of the application, a plurality of gabions are placed at the bottom of the water-proof cavity; the first water diversion layer is arranged in the gap between the adjacent gabions and extends into the river channel.
As another embodiment of the application, the second water diversion layer is plugged at the water outlet.
As another example of the present application, the adsorption layer includes zeolite and sepiolite wool containing a microbial community.
As another example of the present application, the microbial community includes ammonifying bacteria and nitrifying bacteria.
As another embodiment of the present application, the eluviation layer includes a plurality of gravels.
As another embodiment of the present application, the denitrification layer comprises a plurality of ceramic particles.
As another embodiment of the present application, the water absorption layer, the first water diversion layer, and the second water diversion layer each include a super absorbent resin, and the water absorption layer is configured to mix and supply the fluid diverted from the first water diversion layer and the second water diversion layer to the microbial degradation layer.
As another embodiment herein, the biodegradable layer comprises sphingomonas.
As another embodiment of the present application, an outflow port for communicating with the water inlet is formed in the flow guide pipe, a cover net is fixed on the outflow port, and the floating ball is disposed inside the cover net.
The ecological bank protection purification system provided by the invention has the beneficial effects that: compared with the prior art, the ecological bank protection and purification system has the advantages that the plurality of water-proof cavities are arranged in the foundation pit of the river bank slope, the guide pipes are arranged at the tops of the plurality of water-proof cavities, the floating balls for opening and closing the water inlets are arranged on the guide pipes, and sewage can be conveyed to the plurality of water-proof cavities arranged along the length direction of the river channel through the guide pipes. The top and the bottom of the water-proof cavity are respectively provided with a water inlet and a water outlet; two superfine fiber layers are sequentially placed along the length direction of the waterproof cavity; two superfine fiber layers and water proof cavity enclose and establish into three reaction tank, and it has adsorbed layer, eluviation layer and denitrification layer to fill in proper order in the three reaction tank that from top to bottom arranges. The side surface of the water-proof cavity far away from the foundation pit is paved with a water absorption layer, the bottom of the water absorption layer is connected with a first water diversion layer and a second water diversion layer, the first water diversion layer is used for guiding the liquid in the river channel, and the second water diversion layer is used for guiding the liquid in the water outlet. And a microbial degradation layer is laid on the water absorption layer, and the liquid flowing from the water absorption layer is biodegraded through the microbial degradation layer. The soil layer is laid on the microbial degradation layer, and plants are planted on the soil layer.
In this application, the sewage that is carried by the honeycomb duct passes through adsorbed layer, eluviation layer and denitrification layer in proper order, and nitrogen phosphorus pollutant in the middle of can the effective absorption water reaches the effluent standard. The first water diversion layer and the second water diversion layer respectively conduct liquid in a river channel and sewage after treatment, the two liquids are mixed in the water absorption layer and conveyed to the microbial degradation layer, organic matters can be decomposed into inorganic matters through biodegradation, and nutrients are provided for the soil layer above the organic matters. Along with the loss of water in the soil layer, because the water absorption layer, the first water diversion layer and the second water diversion layer have a capillary phenomenon, the liquid in the water absorption layer can continuously move upwards without external force and carry the nutrients such as inorganic matters after biodegradation to supply to plants, thereby ensuring the normal operation of the whole system.
Drawings
In order to more clearly illustrate the technical solutions in the embodiments of the present invention, the drawings needed for the embodiments or the prior art descriptions will be briefly described below, and it is obvious that the drawings in the following description are only some embodiments of the present invention, and it is obvious for those skilled in the art to obtain other drawings without creative efforts.
Fig. 1 is a schematic structural diagram of an ecological bank protection purification system provided by an embodiment of the invention;
fig. 2 is a schematic connection diagram of the draft tube and the cover member according to the embodiment of the present invention.
In the figure: 1. a water-proof cavity; 2. a water inlet; 3. a flow guide pipe; 4. an adsorption layer; 5. a microfiber layer; 6. leaching layer; 7. a denitrification layer; 8. a water outlet; 9. a gabion; 10. a second drainage layer; 11. a microbial degradation layer; 12. a water-absorbing layer; 13. a soil layer; 14. an outflow port; 15. a floating ball; 16. a cover net; 17. a first drainage layer.
Detailed Description
In order to make the technical problems, technical solutions and advantageous effects to be solved by the present invention more clearly apparent, the present invention is further described in detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.
Referring to fig. 1 and 2, the ecological bank protection purification system provided by the present invention will now be described. Ecological bank protection clean system includes: a plurality of water-proof cavities 1, a draft tube 3, a water absorbing layer 12, a microbial degradation layer 11 and a soil layer 13. The plurality of water-resisting cavities 1 are arranged in foundation pits of a bank slope of the river channel and are distributed along the length direction of the river channel; the top and the bottom of the water-proof cavity 1 are respectively provided with a water inlet 2 and a water outlet 8; two superfine fiber layers 5 are sequentially arranged along the length direction of the waterproof cavity 1; two superfine fiber layers 5 and the water-proof cavity 1 are enclosed into three reaction tanks, and an adsorption layer 4, an eluviation layer 6 and a denitrification layer 7 are sequentially filled in the three reaction tanks which are arranged from top to bottom. The honeycomb duct 3 is located the top of a plurality of water proof cavity 1 and is used for carrying sewage to water proof cavity, installs a plurality of floater 15 that are used for opening and close water inlet 2 on the honeycomb duct 3. The layer 12 that absorbs water is laid on the side of keeping away from the foundation ditch at water-proof cavity 1, and the layer 12 bottom that absorbs water is connected with first drainage layer 17 and second drainage layer 10, and first drainage layer 17 is used for the liquid in drainage river course, and second drainage layer 10 is used for the liquid of drainage delivery port 8. The microbial degradation layer 11 is laid on the water absorbing layer 12, and the microbial degradation layer 11 is used for performing biodegradation on liquid flowing in from the water absorbing layer 12. The soil layer 13 is laid on the microbial degradation layer 11 and used for planting plants.
The ecological bank protection purification system provided by the invention has the beneficial effects that: compared with the prior art, the ecological bank protection and purification system has the advantages that the plurality of water-proof cavities 1 are arranged in the foundation pit of the river bank slope, the guide pipes 3 are arranged at the tops of the plurality of water-proof cavities 1, the floating balls 15 for opening and closing the water inlets 2 are arranged on the guide pipes 3, and sewage can be conveyed to the plurality of water-proof cavities 1 arranged along the length direction of the river channel through the arrangement of the guide pipes 3. The top and the bottom of the water-proof cavity 1 are respectively provided with a water inlet 2 and a water outlet 8; two superfine fiber layers 5 are sequentially arranged along the length direction of the waterproof cavity 1; two superfine fiber layers 5 and the water-proof cavity 1 are enclosed into three reaction tanks, and an adsorption layer 4, an eluviation layer 6 and a denitrification layer 7 are sequentially filled in the three reaction tanks which are arranged from top to bottom. The water-proof cavity 1 is laid on the side far away from the foundation pit and is provided with a water absorption layer 12, the bottom of the water absorption layer 12 is connected with a first water diversion layer 17 and a second water diversion layer 10, the first water diversion layer 17 is used for guiding the liquid in the river channel, and the second water diversion layer 10 is used for guiding the liquid in the water outlet 8. The water absorbing layer 12 is paved with a microbial degradation layer 11, and the liquid flowing from the water absorbing layer 12 is biodegraded through the microbial degradation layer 11. The soil layer 13 is laid on the microbial degradation layer 11, and plants are planted on the soil layer 13.
In this application, the sewage that is carried by honeycomb duct 3 passes through adsorbed layer 4, eluviation layer 6 and denitrification layer 7 in proper order, and nitrogen phosphorus pollutant in the middle of can the effective absorption water reaches the water standard. The first drainage layer 17 and the second drainage layer 10 respectively drain the liquid in the river channel and the treated sewage, the two liquids are mixed in the water absorption layer 12 and are conveyed to the microbial degradation layer 11, organic matters can be decomposed into inorganic matters through biodegradation, and nutrients are provided for the soil layer 13 above the organic matters. Along with the loss of water in the soil layer 13, because the water absorption layer 12, the first water diversion layer 17 and the second water diversion layer 10 have a capillary phenomenon, the liquid in the water absorption layer 12 can continuously move upwards without external force and carry the nutrients such as inorganic matters after biodegradation and the like to supply to plants, thereby ensuring the normal operation of the whole system.
As a specific embodiment of the ecological bank protection purification system provided by the invention, please refer to fig. 1, a plurality of gabions 9 are placed at the bottom of a water-proof cavity 1; a first drainage layer 17 is provided in the gap between adjacent gabions 9 and extends into the channel. The gabion 9 is a form of an ecological grid structure, and is a cage filled with stones provided to prevent a river bank or a structure from being washed by water currents. The gabion 9 is located at the bottom of the waterproof cavity 1, and the waterproof cavity 1 is supported through the gabion 9. First drainage layer 17 is located the inside of gabion 9 in this application, and first drainage layer 17 can set up the clearance department at two gabions 9, has avoided because first drainage layer 17 places when outside, and the external environment is to the weathering and the destruction of first drainage layer 17. First drainage layer 17 one end is connected on layer 12 absorbs water, the other end is located the bottom in river course, first drainage layer 17 is carried the water in the river course to layer 12 that absorbs water with the help of capillary phenomenon, because the evaporation of moisture and the absorption of plant in the soil horizon 13, the liquid that absorbs water layer 12 can upwards move, get into microbial degradation layer 11, behind the degradation of microbial degradation layer 11, the inorganic matter after the liquid can carry the biodegradation carries to the plant, thereby can provide sufficient nutrient for the plant. The top of gabion 9 leans on soil horizon 13 and microbial degradation layer 11 in this application, guarantees the stability of soil horizon 13 and microbial degradation layer 11 structure through gabion 9, prevents to produce the slippage.
In this application, because after the processing of adsorbed layer 4, eluviation layer 6 and denitrification layer 7, the corresponding reduction of the content of nitrogen and phosphorus in the sewage, but the content of organic matter does not take place obvious change, consequently if sewage after the direct processing completion lets in microbial degradation layer 11 this moment, because the rate that external organic matter concentration is higher can lead to the interior biodegradable of microbial degradation layer 11 reduces, the result that finally leads to does, the organic matter is not handled the completion and is absorbed in soil horizon 13 promptly, make the plant growth potential slow down, lead to the withering of plant when serious. Consequently when 8 sewage of delivery port are led to one of them drainage layer 10, by the liquid in another drainage layer 10 drainage river course, because organic matter content is lower in the river course aquatic, through diluting sewage, not only guaranteed going on of biodegradation continuously, avoided the too big injury that causes the plant of organic matter content simultaneously.
In this application, adsorbed layer 4, eluviation layer 6 and denitrification layer 7 set gradually according to upper and lower order, through water proof cavity 1 and the superfine fiber layer 5 that sets up, can guarantee that sewage flows through adsorbed layer 4 in proper order, eluviation layer 6 and denitrification layer 7, because water proof cavity 1 has waterproof performance, avoided in sewage directly gets into the soil of river course bank slope from adsorbed layer 4 or eluviation layer 6, avoided the pollution of river course.
Referring to fig. 1, a water outlet 8 is disposed at an open end of the bottom of a water-proof cavity 1, and a water diversion layer 10 is plugged at the water outlet 8. The bottom of the water-proof cavity 1 is open, the open end of the water-proof cavity 1 is a water outlet 8, the water diversion layer 10 is plugged on the water outlet 8, and the water diversion layer 10 abuts against the gabion 9. The sewage filtered by the adsorption layer 4, the leaching layer 6 and the denitrification layer 7 all flows into the drainage layer 10, so that the normal operation of the system is ensured.
As a specific embodiment of the ecological bank protection purification system provided by the present invention, the adsorption layer 4 includes zeolite and sepiolite wool containing microbial communities. The adsorption layer 4 is of a layered structure and is arranged according to the flow of the sewage conveyed by the flow guide pipe 3. Zeolite catalyst for ammonium nitrogenThe zeolite has huge specific surface area, is an ideal microbial carrier, and fixes ammonifying bacteria and nitrifying bacteria in the zeolite during construction so as to further remove the ammonia nitrogen. The sepiolite wool is flocculent and belongs to phyllosilicate, and the total surface area of the sepiolite is 800-900 m calculated according to the structural model of Brown and Prisinge2Per g, internal surface area 500m2Per g, external surface area 400m2The water content of the sepiolite can reach 200-250% of the self weight at most, so that the hydraulic retention and the retention time are prolonged, the purification treatment procedure is prolonged, and the purification efficiency of biochemical reaction is improved. The zeolite has a particle size of 3-6mm, and the mixing ratio of the zeolite to the sepiolite wool is 1: microorganisms are attached to the surfaces of the zeolite, and the main purposes are to remove phosphorus in a water body and convert ammonia nitrogen in the water into nitrate substances for subsequent treatment.
As a specific embodiment of the ecological bank protection purification system provided by the present invention, the microbial community comprises ammoniated bacteria and nitrifying bacteria. The main purposes of setting corresponding strains are to remove water P and convert N element in water into NO3-class N; in the purification treatment process, ammonifying bacteria and nitrifying bacteria are easily formed in the adsorption layer 4 as dominant microbial communities, the propagation speed is high, the most important biochemical reaction center in the ecological bank protection purification system is formed, and organic nitrogen is firstly converted into ammonia nitrogen NH through the ammonifying bacteria4N and fixed by zeolites and subsequently converted again by nitrifying bacteria into nitrate nitrogen NO3N, nitrate nitrogen does not participate in any reaction at this stage.
As a specific embodiment of the ecological bank protection purification system provided by the present invention, the eluviation layer 6 includes a plurality of gravels. The particle size of the gravel is 5-20 mm; the gravel can stabilize the layer structure and play a role in adsorption and filtration, and further accelerate the nitrate nitrogen to rapidly enter the denitrification layer 7.
Referring to fig. 1, as an embodiment of the ecological bank protection purification system provided by the present invention, the denitrification layer 7 includes a plurality of ceramsite. Each ceramsite contains denitrifying bacteria. The ceramsite has various excellent properties, such as porous inside, huge specific surface area, small density, high strength and firmness, so that the ceramsite has the characteristics of light weight, strong adsorption force, easiness in microorganism attachment, firmness, corrosion resistance, freezing resistance and the like, and denitrifying bacteria are fixed in the ceramsite during construction; the denitrification layer 7 is positioned below the leaching layer 6 and has the function of water guiding and draining, in addition, as the denitrification layer 7 is positioned at the bottommost part of the ecological bank protection purification system, the dissolved oxygen concentration of the denitrification layer 7 is extremely low, and meanwhile, the ceramsite provides abundant attachment sites for microorganisms, so that a microbial community taking denitrifying bacteria as a main part is easily formed in the denitrification layer 7, and the leached nitrate nitrogen is converted into nitrogen under the action of the denitrifying bacteria, so that the aim of removing nitrogen is fulfilled.
Referring to fig. 1, the water absorbing layer 12, the first drainage layer 17 and the second drainage layer 10 all include super absorbent resin, and the water absorbing layer 12 is used for mixing the liquid drained from the first drainage layer 17 and the second drainage layer 10 and supplying the mixed liquid to the microbial degradation layer 11. The thickness of the high water absorption resin layer is 2-4 cm; the main purpose of the super absorbent resin layer is to provide moisture for the biodegradable layer 11 laid on the water absorbing layer 12, the moisture of the biodegradable layer 11 can increase the biodegradation rate of bacteria after being increased, and the moisture of the biodegradable layer 11 can directly ensure the sufficient moisture in the soil layer 13.
As a specific embodiment of the ecological bank protection purification system provided by the present invention, the microbial degradation layer 11 comprises sphingomonas. Adopting a nonionic surfactant to form a cloud point system at a temperature lower than that of the hydrophobic organic matters degraded by the microorganisms; the cloud point system is used as a medium for degrading hydrophobic organic matters by microorganisms, and the hydrophobic organic matters in the environment are extracted and solubilized into a degradation culture medium to realize degradation of the hydrophobic organic matters.
By adopting the technical scheme, the cloud point system is formed and is used as a medium for degrading the hydrophobic organic matters by the microorganisms, and the hydrophobic organic matters are used as nutrition and energy of the microorganisms to be utilized along with the extraction and solubilization of the hydrophobic organic matters in the environment into a degradation culture medium, so that the purposes of degradation and pollution treatment of the hydrophobic organic matters are realized. In the invention, the key point of adopting the cloud point system to realize the microbial degradation of the hydrophobic organic matters is to improve the bioavailability of the organic matters and maintain the degradation activity of the microorganisms. The hydrophobic organic matter is selected from one or more of polycyclic aromatic hydrocarbon and halogenated polycyclic aromatic hydrocarbon. Polycyclic aromatic hydrocarbons refer to 2-4 ring aromatic hydrocarbons.
The bioavailability of the hydrophobic organic matter is improved by forming the cloud point system, the application of the cloud point system in the degradation of the hydrophobic organic pollutant is realized, and the environmental pollution treatment is facilitated. The cloud point system extracts hydrophobic organic matters which are difficult to dissolve in water into the coacervate phase to form dissolved organic matters, and because the concentration of the organic matters in the coacervate phase is higher than that of the organic matters in the water phase, the organic matters are diffused and transferred from the coacervate phase to the water phase until the coacervate phase is balanced according to a two-phase balance principle. On one hand, the concentration of the organic matter substrate in the water environment where the microorganism is positioned is obviously increased, and the biodegradation efficiency of the microorganism is obviously improved; on the other hand, as the organic matters in the water environment are degraded by microorganisms, the organic matters in the cloud point system coacervate phase are further diffused and transferred to the water phase, and the balance of the substrate in the two phases is kept, so that the continuous degradation of the organic matters is ensured. The key to this process is that the cloud point system does not affect the microbial degradation activity while changing the bioavailability of hydrophobic organics.
Referring to fig. 2, an outflow port 14 for communicating with the water inlet 2 is formed on the draft tube 3, a cover net 16 is fixed on the outflow port 14, and a floating ball 15 is disposed inside the cover net 16. Be provided with a plurality of water proof cavity 1 in this application, a plurality of water proof cavity 1 set up on the length direction along the river course, in order to make the homoenergetic of a plurality of water proof cavity 1 let in sewage, it is fixed with cover net 16 to be located egress opening 14 department at honeycomb duct 3, a plurality of through-holes have been seted up on the cover net 16, floater 15 slides and locates in the cover net 16, float in cover net 16 with the help of buoyancy floater 15 of the interior liquid of water proof cavity 1, when the liquid level is higher in water proof cavity 1, floater 15 blocks up egress opening 14, the sewage flows to next water proof cavity 1. The length of honeycomb duct 3 and the corresponding setting of length in river course, honeycomb duct and the traditional irrigation methods of 15 similar agriculture of floater in this application, but the difference lies in that in this application after the moisture reduces in soil horizon 13, can make layer 12 and the diversion layer 10 that absorb water and absorb liquid, after water level descends in water proof cavity 1, the cubical switchboard is reopened to can supply sewage, guarantee sewage purification's normal clear.
The present invention is not limited to the above preferred embodiments, and any modifications, equivalent substitutions and improvements made within the spirit and principle of the present invention should be included in the protection scope of the present invention.

Claims (10)

1. Ecological bank protection clean system, its characterized in that includes:
the water-proof cavities are used for being placed in foundation pits of a river bank slope and are arranged along the length direction of the river; the top and the bottom of the waterproof cavity are respectively provided with a water inlet and a water outlet; two superfine fiber layers are sequentially arranged along the length direction of the waterproof cavity; the two superfine fiber layers and the water-proof cavity are enclosed into three reaction tanks, and an adsorption layer, a leaching layer and a denitrification layer are sequentially filled in the three reaction tanks which are arranged from top to bottom;
the drainage pipe is positioned at the tops of the water-proof cavities and used for conveying sewage to the water-proof cavities, and a plurality of floating balls used for opening and closing the water inlets are mounted on the drainage pipe;
the water absorption layer is laid on the side face, far away from the foundation pit, of the water-resisting cavity, the bottom of the water absorption layer is connected with a first water diversion layer and a second water diversion layer, the first water diversion layer is used for guiding liquid of the river channel, and the second water diversion layer is used for guiding liquid of the water outlet;
the microbial degradation layer is laid on the water absorption layer and is used for performing biodegradation on liquid flowing in from the water absorption layer; and
and the soil layer is laid on the microbial degradation layer and is used for planting plants.
2. The ecological bank protection and purification system of claim 1, wherein a plurality of gabions are placed at the bottom of the water-proof cavity; the first water diversion layer is arranged in the gap between the adjacent gabions and extends into the river channel.
3. The ecological bank protection and purification system of claim 1, wherein the second water diversion layer is plugged at the water outlet.
4. The ecological bank protection purification system of claim 1, wherein the adsorption layer comprises zeolite and sepiolite wool containing microbial communities.
5. The ecological bank protection purification system of claim 4, wherein the microbial community comprises ammoniating bacteria and nitrifying bacteria.
6. The ecological bank protection purification system of claim 1, wherein the eluviation layer comprises a plurality of gravels.
7. The ecological bank protection and purification system of claim 1, wherein the denitrification layer comprises a plurality of ceramic particles.
8. The ecological revetment purification system of claim 1, wherein the water-absorbing layer, the first drainage layer and the second drainage layer each comprise a super absorbent resin, and wherein the water-absorbing layer is configured to mix and provide the liquids drained from the first drainage layer and the second drainage layer to the biodegradable layer.
9. The ecological bank protection and purification system of claim 1, wherein the microbial degradation layer comprises sphingomonas.
10. The ecological bank protection and purification system of claim 1, wherein the draft tube is provided with an outflow port for communicating with the water inlet, the outflow port is fixed with a cover net, and the floating ball is arranged inside the cover net.
CN202010366066.8A 2020-04-30 2020-04-30 Ecological bank protection clean system Pending CN111635065A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202010366066.8A CN111635065A (en) 2020-04-30 2020-04-30 Ecological bank protection clean system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202010366066.8A CN111635065A (en) 2020-04-30 2020-04-30 Ecological bank protection clean system

Publications (1)

Publication Number Publication Date
CN111635065A true CN111635065A (en) 2020-09-08

Family

ID=72328284

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010366066.8A Pending CN111635065A (en) 2020-04-30 2020-04-30 Ecological bank protection clean system

Country Status (1)

Country Link
CN (1) CN111635065A (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03262595A (en) * 1990-03-10 1991-11-22 Hokoku Kogyo Co Ltd Equipment for improving water quality of river and water channel or the like
CN105148446A (en) * 2015-08-26 2015-12-16 江西理工大学 Method for extracting microbial degradation hydrophobic organic compound from cloud point system
CN105461072A (en) * 2015-12-29 2016-04-06 岭南新科生态科技研究院(北京)有限公司 Ecological bank revetment purifying system
US20160376181A1 (en) * 2014-03-21 2016-12-29 Nanjing University Ecological Research Institute Of Changshu In-situ purification island structure and the construction method thereof
CN207537311U (en) * 2017-11-15 2018-06-26 天津大学 A kind of automatic control type ecological shore protection system for riverway water quality purification

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03262595A (en) * 1990-03-10 1991-11-22 Hokoku Kogyo Co Ltd Equipment for improving water quality of river and water channel or the like
US20160376181A1 (en) * 2014-03-21 2016-12-29 Nanjing University Ecological Research Institute Of Changshu In-situ purification island structure and the construction method thereof
CN105148446A (en) * 2015-08-26 2015-12-16 江西理工大学 Method for extracting microbial degradation hydrophobic organic compound from cloud point system
CN105461072A (en) * 2015-12-29 2016-04-06 岭南新科生态科技研究院(北京)有限公司 Ecological bank revetment purifying system
CN207537311U (en) * 2017-11-15 2018-06-26 天津大学 A kind of automatic control type ecological shore protection system for riverway water quality purification

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
周宜开: "《中华医学百科全书·环境卫生学》", 31 March 2017, 中国协和医科大学出版社 *
邹小钢: "《环境保护工作创新与发展》", 30 April 2009, 中国地质大学出版社 *

Similar Documents

Publication Publication Date Title
AU2020103451A4 (en) Method for landscape water body regulation and ecological purification of urban and peripheral high-water-table coal mining subsidence areas
CN103215920B (en) Sectored multi-step ecological buffer revetment system
CN112358053A (en) Composite ecological treatment method for intercepting farmland drainage pollutants
CN205313193U (en) System for purifying micro -polluted water flowing to reservoirs (lakes) and repairing ecological wetlands
CN107935307B (en) River water purification system for enhancing biological decomposition through cyclic reoxygenation and implementation method
CN109399800B (en) River and lake runoff pollution cascade control system
CN102001753A (en) Ecological corridor for removing nitrogen and phosphorus of micro-polluted river water and construction method thereof
CN213037496U (en) Partitioned circulating soil infiltration system
CN113354093A (en) River channel restoration method by coupling ecological revetment and aquatic plants
CN107487846B (en) Ecological type hard revetment suitable for variable water level
CN212127909U (en) Artificial wetland deep purification system for treating industrial wastewater
CN204570617U (en) Groin system filled by absorption type gabion box haydite
WO2021098731A1 (en) Wastewater interception centralized treatment system and treatment method for river channel regulation
CN113772822A (en) River and lake ecological restoration system
CN107459142A (en) A kind of ecological ground sills system and construction method for urban landscape rivers
CN104016546B (en) Environment-friendly artificial wetland system for purifying dredging remained water/tail water
CN111635065A (en) Ecological bank protection clean system
CN217479166U (en) In-situ purification device for shallow lake
CN112830642A (en) Novel ecological ditch system for preventing and treating farmland non-point source pollution
CN211770572U (en) Wetland structure between river gravels
CN211090825U (en) Emergent aquatic plant decontaminating planting and fixing device
CN210133936U (en) Utilize ecological concrete's annular view water purification constructed wetland system
CN212102457U (en) Urban heavily polluted river water ecological restoration simulation device
CN113321313A (en) Composite habitat system for improving water quality of high-flow-rate and high-sand-content riverway
CN112759087A (en) Denitrification artificial wetland integrated purification system and sewage ecological purification 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
RJ01 Rejection of invention patent application after publication

Application publication date: 20200908

RJ01 Rejection of invention patent application after publication