CN108715486A - A kind of method of basin pool shoal molecular fluid restoration of the ecosystem - Google Patents

A kind of method of basin pool shoal molecular fluid restoration of the ecosystem Download PDF

Info

Publication number
CN108715486A
CN108715486A CN201810593141.7A CN201810593141A CN108715486A CN 108715486 A CN108715486 A CN 108715486A CN 201810593141 A CN201810593141 A CN 201810593141A CN 108715486 A CN108715486 A CN 108715486A
Authority
CN
China
Prior art keywords
pool
shoal
ecosystem
basin
water
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.)
Granted
Application number
CN201810593141.7A
Other languages
Chinese (zh)
Other versions
CN108715486B (en
Inventor
林映津
刘毅勐
陈雪娇
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.)
Hua Chuan Technology Co Ltd
Original Assignee
Hua Chuan 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 Hua Chuan Technology Co Ltd filed Critical Hua Chuan Technology Co Ltd
Priority to CN201810593141.7A priority Critical patent/CN108715486B/en
Publication of CN108715486A publication Critical patent/CN108715486A/en
Application granted granted Critical
Publication of CN108715486B publication Critical patent/CN108715486B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • 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
    • C02F7/00Aeration of stretches of water
    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B3/00Engineering works in connection with control or use of streams, rivers, coasts, or other marine sites; Sealings or joints for engineering works in general
    • E02B3/02Stream regulation, e.g. breaking up subaqueous rock, cleaning the beds of waterways, directing the water flow
    • 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
    • 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
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical & Material Sciences (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • General Engineering & Computer Science (AREA)
  • Structural Engineering (AREA)
  • Civil Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Ocean & Marine Engineering (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The present invention relates to a kind of methods of basin pool shoal molecular fluid restoration of the ecosystem.It is mainly made of pool, side slope and shoal three parts restorative procedure, before implementing pool shoal restoration of the ecosystem, is first chosen according to the following conditions:Condition 1:It whether there is pool in basin;Condition 2:It whether there is shoal in basin;The total amount of pollutant during the pool is repaired is cut down, and mainly clears up technology, ecological factor control technique and sludge reduction technology by high dissolved oxygen technology, microorganism to realize sludge reduction in basin;Water and soil during the side slope is repaired is firm, mainly realizes that side slope water and soil is firm by being laid with ecological revetment brick and planting water-fast wet plant;The ecosystem during the shoal is repaired is built, and mainly realizes the structure of the ecosystem by building plant ecosystem, structure microbial ecosystem and structure animal ecology system.Realize the healthy and orderly development of microbial ecosystem, water pollutant of effectively degrading.

Description

A kind of method of basin pool shoal molecular fluid restoration of the ecosystem
Technical field
The present invention relates to a kind of pool shoal recovery techniques, and in particular to a kind of basin pool shoal molecular fluid is given birth to The method of state reparation.
Background technology
The qualified discharge concentration of the major part waste discharge such as breeding wastewater, sanitary sewage, the industrial wastewater in basin is above Ground Table quality standard of water environment, some qualified discharge concentration ratio water environment quality standards are higher by more than ten times of even hundreds of times, To cause nutrient concentration in basin largely to be promoted, in order to make basin reach water environment quality standard, basin need to have Higher pollution self-purification capacity, in basin using pool shoal be improve basin self-purification capacity a kind of possible ways.
Flow in basin in pool is slower, and it is good place to go that animal is had a rest that nutriment is abundant, in shoal dissolved oxygen compared with Height, and illumination condition is good provides the production institute that good condition and fish well look for food and lay eggs for the procreation of algae, but with The passage of time and stepping into for pollutant, Dissolved Oxygen in Water content declines to a great extent in pool, and anaerobic state is presented in bottom, Bed mud is promoted largely to deposit, pool volume is gradually reduced, and a large amount of nutritive salt in upstream and suspended matter flow into shoal, and shoal is promoted to become silted up Product, raises the water surface or basin is caused to change its course, endanger water body and the bank ecosystem.
In basin there is the self-purification capacity that basin can be improved in the interaction in the good pool shoal of function, enrich the ecology in basin Diversity.Therefore, pool and shoal are built in basin has preferable repairing effect to impaired watershed ecosystem.Mesh Before, the utilization in pool shoal is essentially consisted on the structure to pool shoal, since pool shoal is to the reparation category of the ecosystem Pool shoal is only built for the water body that seriously polluted and needs are repaired in short term in a slow and very long process Cannot have good repairing effect, and in the case where water quality is poor, structure pool can cause pool bottom anaerobism, oxidation also Former current potential reduces, and siltation bed mud largely discharges polluter, and the indexs content such as water body ammonia nitrogen, total phosphorus is significantly increased, not only cannot Play the role of repairing water body, also water pollution situation can be made more serious.Therefore, to taking certain quickening water on pool shoal The measure of body reparation can improve pool shoal Effect of Ecological Restoration more preferably, faster.
Invention content
In order to overcome the above-mentioned deficiencies of the prior art, the object of the present invention is to provide a kind of basin pool shoal molecules The method of fluid restoration of the ecosystem.It can realize the healthy and orderly development of microbial ecosystem, so as to permanently effective degradation Water pollutant promotes water pollution salinity to continuously decrease and maintains within the scope of low concentration for a long time;Realize water body plant The high-efficient development of the ecosystem makes plant retain external source pollution while absorbing water pollutant purifying water body water quality, from interior Two aspects of external source improve water quality;The recovery for realizing animal ecology system can promote basin realizing purification of water quality There is certain catch again simultaneously, watershed ecosystem is made to have both ecological benefits and economic benefit.
The purpose of the present invention is what is be achieved through the following technical solutions:A kind of molecular fluid restoration of the ecosystem of basin pool shoal Method, be mainly made of pool, side slope and shoal three parts restorative procedure, before implementing pool shoal restoration of the ecosystem, first press It is chosen according to the following conditions:
Condition 1:It whether there is pool in basin;
Condition 2:It whether there is shoal in basin;
If there is no pools just to form pool region by excavating pool or building the engineering measure of groynes in basin;If basin It is interior there is no shoal just by excavate pool the earthwork landfill reduce basin channel gradient or build submerged breakwater engineering measure come Shoal region is formed, the total amount of pollutant during the pool is repaired is cut down, and is mainly cleared up by high dissolved oxygen technology, microorganism Technology, ecological factor control technique and sludge reduction technology realize sludge reduction in basin;During the side slope is repaired Water and soil it is firm, mainly realize that side slope water and soil is firm by being laid with ecological revetment brick and planting water-fast wet plant;Described The ecosystem during shoal is repaired is built, and is mainly passed through and is built plant ecosystem, structure microbial ecosystem and structure Animal ecology system realizes the structure of the ecosystem;High dissolved oxygen technology in the pool reparation is mainly filled by nanometer dissolved oxygen Set, high dissolved oxygen generating device, high dissolved oxygen generating device be authorize the device being related in patent of invention ZL 201110455752.3, Microbubble and micro-nano bubble diffusing apparatus, microbubble and micro-nano bubble diffusing apparatus are to authorize patent of invention ZL 201110180368.7 the device that is inside related to is realized;Microorganism resolution technology, which is added by microorganism and had, adjusts ecological factor The ecologic reef of function has and adjusts the ecologic reef of ecological factor function to authorize utility model patent ZL 201620993812.5 The content that is inside related to is realized;Ecological factor control technique is by ecological factor and gene expression nanometer adjusting device, ecological factor And gene expression nanometer adjusting device is to authorize the device being related in patent of invention ZL 201510010303.6 and given birth to adjusting State is realized because of the ecologic reef of subfunction;Sludge reduction technology is by sludge reducing high-efficiency biochemical treatment device, mud decrement It is that the device being related in patent of invention ZL 201110455813.6 is authorized to realize to change high-efficiency biochemical treatment device;The height Dissolved oxygen generating device is ground installation, and ultramicro air bubble dissolved oxygen outlet pipe is connected with the air inlet pipe of underwater nanometer oxygen-dissolving apparatus, nanometer The quantity of oxygen-dissolving apparatus be 3 or 3 or more, nanometer oxygen-dissolving apparatus cloth dot shape be triangle or polygon, microbubble and Micro-nano bubble diffusing apparatus is mounted on the centre of nanometer oxygen-dissolving apparatus institute cloth dot shape;Ground microbiological is tamed in culture pond The microorganism that microorganism in situ is added in the ecologic reef with adjusting ecological factor function adds Guan Houzai and is released via microorganism Discharge hole discharges into water body;Ecological factor and gene expression nanometer adjusting device interior tracheae with adjusting ecological factor function The appendix of ecologic reef connects;It adopts mud pipe nozzle to stretch into bed mud, adopt at mud pipe and suction pump and sludge reducing high-efficiency biochemistry Manage biological fluidized bed connection in device;The side slope is repaired mainly by being laid with ecological revetment brick, ecological revetment brick in side slope For application number:The brick body being related in 201810314574.4 and the water-fast wet plant for being planted in ecological revetment brick planting intracavitary To realize;Plant ecosystem structure is mainly net by purification of water quality basket implants and shoal sprinkling biology during the shoal is repaired Change system is realized;Microbial ecosystem structure is mainly by sorbing material in purification of water quality basket and with adjusting ecological factor The ecologic reef of function is realized;Animal ecology system structure is mainly introduced by local aquatic animal species and with adjusting ecology It is realized because of the ecologic reef of subfunction;The shoal sprinkling biological purification system mainly extracts water in pool by suction pump Body flows into sandy beach area in shoal through pipeline, and sandy beach area pipeline is equipped with atomization mouth, and pool area water body is atomized into small through atomization mouth The droplet of grain size is sprayed in the area of sandy beach in purification of water quality basket implants and sorbing material, and bottom is equipped in purification of water quality basket One layer of sorbing material, sorbing material are zeolite or activated carbon or biologic packing material, and shoal has the life for adjusting ecological factor function State reef is also connected with the ecological factor of pool and gene expression nanometer adjusting device and microbial acclimation culture pond.
By adopting the above-described technical solution, the present invention can promote pool shoal to develop towards with good direction, Accelerate speed of the pool shoal to water ecosystem reparation.In pool reparation, by improving Dissolved Oxygen in Water, improve water body Environment-ecological Factors accelerate resolution of the microorganism to water nutrition, and take sludge reduction measure, realize to water body The reduction of the total amount of pollutant, and the microorganism added is Culture in situ acclimated microorganism, introduces, is not easy pair without external flora Water body causes secondary pollution;In side slope reparation, prevent the soil in side slope in rainwash by being laid with ecological revetment brick It is lower to enter water body and bring a large amount of nutriment in soil into water body, it is upper water-fast in the plantation of ecological revetment brick planting intracavitary On the one hand wet plant can have better fixed function, another aspect plant that can retain rainwater with side slope soil, mitigate rainwater Soil washes away, and reduces the external source pollution of water body, and the water body to realize side slope is firm and reduces the pollution of water body external source;Shallow During beach is repaired, mainly pass through the structure of the structure and animal ecology system of structure, microbial ecosystem to plant ecosystem It builds, in conjunction with the reclamation activities of pool and side slope, to promote the structure of watershed ecosystem.Most by the reparation of the above measure The healthy and orderly development of microbial ecosystem is realized eventually, so as to permanently effective degradation water pollutant, promotes water body Pollution salinity is continuously decreased and is maintained within the scope of low concentration for a long time;Realize the efficient hair of water body plant ecosystem Exhibition makes plant retain external source while absorbing water pollutant purifying water body water quality and pollutes, the improvement in terms of interior external source two Water quality;The recovery of animal ecology system is realized, basin can be promoted to have again while realizing purification of water quality certain Catch makes watershed ecosystem have both ecological benefits and economic benefit.
Pool shoal of the present invention ecological reestablishment has significant repairing effect to various polluted-waters, to water The reparation of body ecological environment has preferable economic benefit, social benefit and ecological benefits.
Description of the drawings
Fig. 1 is a kind of method flow schematic diagram of basin pool shoal molecular fluid restoration of the ecosystem of the invention;
Fig. 2 be a kind of basin pool shoal molecular fluid restoration of the ecosystem of the invention method in side slope and sandy beach area measure structure show It is intended to;
Fig. 3 be a kind of basin pool shoal molecular fluid restoration of the ecosystem of the invention method in purification of water quality basket structural schematic diagram;
Fig. 4 be a kind of basin pool shoal molecular fluid restoration of the ecosystem of the invention method in pool reclamation activities structural representation Figure;
Fig. 5 be a kind of basin pool shoal molecular fluid restoration of the ecosystem of the invention method in shoal reclamation activities structural representation Figure.
In figure, 1- pools;The shoals 2-;The sandy beaches 3- area;4- side slopes;5- suction pumps;6- pipelines;7- is atomized mouth;8- ecologies are protected Slope brick;9- purification of water quality baskets;10- sorbing materials;11- high dissolved oxygen generating devices;12- ultramicro air bubble dissolved oxygen outlet pipes;13- sludge subtracts Quantify high-efficiency biochemical treatment device;14- biological fluidized beds;15- suction pumps;16- nanometers of oxygen-dissolving apparatus;17- air inlet pipe;18- is micro- Bubble and micro-nano bubble diffusing apparatus;19- has the ecologic reef for adjusting ecological factor function;20- appendixs;21- microorganisms Add pipe;22- Microbiological releases hole;23- microbial acclimation culture ponds;24- ecological factors and gene expression nanometer adjusting device; 25- tracheaes;26- adopts mud pipe.
Specific implementation method
Below in conjunction with the accompanying drawings, the present invention is further illustrated.Specific embodiment described herein is only used for explaining this hair It is bright but not as a limitation of the invention.
Embodiment
Such as Fig. 1, shown in 2,3,4,5, a kind of method of basin pool shoal molecular fluid restoration of the ecosystem, mainly by pool 1, Side slope 4 and 2 three parts restorative procedure of shoal composition are first selected according to the following conditions before implementing pool shoal restoration of the ecosystem It takes:
Condition 1:It whether there is pool 1 in basin;
Condition 2:It whether there is shoal 2 in basin;
If there is no pools 1 just to form pool region by excavating pool 1 or building the engineering measure of groynes in basin;If stream The engineering for just reducing basin channel gradient or construction submerged breakwater by excavating the earthwork landfill of pool 1 there is no shoal 2 in domain is arranged It applies to form 2 region of shoal, it is characterized in that the total amount of pollutant during the pool 1 is repaired is cut down, mainly passes through high dissolved oxygen Technology, microorganism clear up technology, ecological factor control technique and sludge reduction technology to realize sludge reduction in basin;Institute Water and soil during the side slope 4 stated is repaired is firm, mainly realizes side slope by being laid with ecological revetment brick and planting water-fast wet plant Water and soil is firm;The ecosystem during the shoal 2 is repaired is built, and is mainly passed through and is built plant ecosystem, the micro- life of structure The object ecosystem realizes the structure of the ecosystem with structure animal ecology system.
High dissolved oxygen technology in the reparation of pool 1 is high mainly by nanometer oxygen-dissolving apparatus 16, high dissolved oxygen generating device 11 Dissolved oxygen generating device 11 is to authorize device, microbubble and the micro-nano bubble being related in patent of invention ZL 201110455752.3 Disperser 18, microbubble and micro-nano bubble diffusing apparatus 18 are to authorize to be related in patent of invention ZL 201110180368.7 Device realize;Microorganism resolution technology is added by microorganism and with the ecologic reef 19 for adjusting ecological factor function, is had The ecologic reef 19 for adjusting ecological factor function is that the content being related in utility model patent ZL 201620993812.5 is authorized to come in fact It is existing;Ecological factor control technique is by ecological factor and gene expression nanometer adjusting device 24, ecological factor and gene expression nanometer Adjusting device 24 is to authorize the device being related in patent of invention ZL 201510010303.6 and with adjusting ecological factor function Ecologic reef 19 is realized;Sludge reduction technology is by sludge reducing high-efficiency biochemical treatment device 13, sludge reducing high-efficiency life It is that the device being related in patent of invention ZL 201110455813.6 is authorized to realize to change processing unit 13.
The high dissolved oxygen generating device 11 is ground installation, and ultramicro air bubble dissolved oxygen outlet pipe 12 is filled with underwater nanometer dissolved oxygen It sets 16 air inlet pipe 17 to be connected, the quantity of nanometer oxygen-dissolving apparatus 16 is 3 or 3 or more, 16 cloth dot shape of nanometer oxygen-dissolving apparatus For triangle or polygon, microbubble and micro-nano bubble diffusing apparatus 18 are mounted on 16 cloth dot shapes of nanometer oxygen-dissolving apparatus Centre;Microorganism in situ in ground microbiological domestication culture pond 23 is added to the ecologic reef for adjusting ecological factor function Microorganism in 19, which adds, releases 22 via Microbiological release hole again after pipe 21 and puts into water body;Ecological factor and gene expression nanometer 24 interior tracheae 25 of adjusting device is connect with the appendix 21 with the ecologic reef 19 for adjusting ecological factor function;Adopt 26 nozzle of mud pipe It stretches into bed mud, adopts mud pipe 26 and connect with biological fluidized bed 14 in suction pump 15 and sludge reducing high-efficiency biochemical treatment device 13 It connects.
The side slope 4 is repaired mainly by being laid with ecological revetment brick 8 in side slope, and ecological revetment brick 8 is application number: The brick body that is related in 201810314574.4 and the water-fast wet plant of 8 planting intracavitary of ecological revetment brick is planted in realize.
Plant ecosystem structure is mainly by 9 implants of purification of water quality basket and shoal sprinkling life during the shoal 2 is repaired Object purification system is realized;Microbial ecosystem structure is mainly by sorbing material 10 in purification of water quality basket 9 and with adjusting The ecologic reef 19 of ecological factor function is realized;Animal ecology system structure is mainly introduced and is had by local aquatic animal species Have and adjusts the ecologic reef 19 of ecological factor function to realize.
The shoal sprinkling biological purification system mainly extracts water body in pool 1 by suction pump 5, is flowed into through pipeline 6 Sandy beach area 3 in shoal 2,3 pipeline 6 of sandy beach area are equipped with atomization mouth 7, and 1 area's water body of pool is atomized into nominal particle size through being atomized mouth 7 Droplet is sprayed in sandy beach area 3 in 9 implants of purification of water quality basket and sorbing material 10, and bottom is equipped with one in purification of water quality basket 9 Layer sorbing material 10, sorbing material 10 are zeolite or activated carbon or biologic packing material, and having for shoal adjusts ecological factor function Ecologic reef 19 is also connected with the ecological factor of pool and gene expression nanometer adjusting device 24 and microbial acclimation culture pond 23.
Effect example one:
Selection is implemented in somewhere basin, the long 23.2km in river, drainage area 101km2.Since the village flowed through is more, bank Sanitary sewage is largely discharged into, and body eutrophication is serious, and transparency is relatively low.
In the basin, upstream vicinity has a primary pool, the long 70m of the pool, width 15m, depth 2m, the pool not to do any work Journey measure, the control group as the effect example;Pool, the long 100m of the pool, width are formed by ponding above the lower reaches 10m, depth 2m, there are shoals for downstream pool lower section, which is handled using pool shoal ecological reestablishment, as the effect The experimental group of fruit example.
Laid in the pool of experimental group 1 group of microbubble and micro-nano bubble diffusing apparatus and 20 groups have adjust ecology because The ecologic reef of subfunction, contains 1 group of nanometer oxygen-dissolving apparatus in every group of ecologic reef, 1 group of microorganism adds unit, and bank is laid with 1 group of ecological factor and gene expression nanometer adjusting device and 1 group of ground microbiological tame culture pond, due to the pool sludge thickness It is smaller, without carrying out sludge reduction, therefore, sludge reduction technology is not used, 10 groups of lifes are laid in the shoal of experimental group The state factor and gene expression nanometer adjusting device, slope ecological is more complete, without taking side slope recovery technique.
Implement 0 day in the present invention(On March 17th, 2018), which is detected, is detected Structure is as shown in table 1:
As shown in Table 1, experimental group(Downstream pool)Ammonia nitrogen compares control group(Upstream pool)High by 11.18%, experimental group total phosphorus is than control High by 7.33%, the experimental group dissolved oxygen lower than control group 3.57% of group.
30 days after the present invention is implemented(On April 16th, 2018), which is carried out second Detection, detection structure are as shown in table 2:
By Tables 1 and 2 it is found that control group after 30 days, ammonia nitrogen decline 21.06%, total phosphorus decline 11.26%, dissolved oxygen promoted 40.87%, the decline of control group water quality is since external source pollution enters reduction during this period and a large amount of of rainfall rainwater enter.
After implementing 30 days, experimental group ammonia nitrogen lower than control group 34.27%, experimental group total phosphorus lower than control group 30.68%, experiment Group dissolved oxygen is higher than control group by 19.15%, it can be seen that, after implementing 30 days, experimental group water quality is promoted notable.Although control group water Matter increases, and experimental group water quality can be made to be promoted, but before not implementing the technology, ammonia nitrogen in control group water body and Total phosphorus content is apparently higher than control group, and the dissolved oxygen content in control group water body is less than control group, but is tested after implementing the technology The content of group ammonia nitrogen and total phosphorus is substantially less than control group, and experimental group dissolved oxygen content is significantly higher than control group.
60 days after the present invention is implemented(On May 16th, 2018), third time is carried out to two groups of pool water quality indexs Detection, detection structure are as shown in table 3:
By table 1 and table 3 comparison it is found that control group after 60 days, ammonia nitrogen decline 24.65%, total phosphorus decline 30.95%, dissolved oxygen drop Low 2.38%, control group water body is persistently promoted during implementation, it may be possible to due to the lasting reduction that external source pollutes during implementation.
Experimental group is after implementing 60 days, and experimental group ammonia nitrogen lower than control group 43.50%, experimental group total phosphorus is lower than control group 61.10%, experimental group dissolved oxygen is higher than control group by 151.22%, it can be seen that, after implementing 60 days, it is high that experimental group water quality promotes effect Water quality promotes effect after implementing 30 days, and dissolved oxygen promotes effect highly significant, illustrates that the implementation of the present invention can continue height The promotion water quality of effect.
In short, upstream water quality is to influence the major reason of downstream water matter, in the case of no any measure, downstream water quality Slightly it is inferior to upstream water quality, and the invention is implemented to promote water quality to better than upstream water quality in the poor downstream of water quality situation Under state, therefore, the implementation present invention can effectively improve water quality in pool shoal.
In conclusion the operation principle of the present invention be by a microbubble and micro-nano disperser with surrounding is multiple receives The combination of rice oxygen-dissolving apparatus, can make the water body containing microbubble and micro-nano bubble form the fluid recycled up and down, and it is molten to improve water body Solve oxygen;High dissolved oxygen generating device is the ultramicro air bubble that nanometer oxygen-dissolving apparatus provides, while improving Dissolved Oxygen in Water, due to gas There are a pressure processes in the forming process of bubble, thus bubble enter water body rupture moment can give off energy, it is this Energy can make bubble, and nearby water body generates high temperature and pressure, can degrade to some hydrophobicities, nonpolarity, volatile substance, In addition, this high temperature and pressure can be such that some hydrones crack, the radical ion with strong oxidizing property is generated, it can be to organic matter It degrades.
Microbubble and micro-nano disperser are formed by circulation of fluid, can be by the nutritive salt of water surface, organic matter Etc. water bottom is brought into, decomposition sorption enhanced is carried out via the aerobic microbiological in bed mud, further, by water body add through The sediment in-situ aerobic microbiological for cultivating domestication, can accelerate the decomposition sorption enhanced to water nutrition, organic matter etc., reduce Water pollutant concentration;And it is big to can be very good immobilized breeding with the artificial aquatic weed in the ecologic reef for adjusting ecological factor function The microorganism of amount makes a large amount of microorganisms downstream spread under the action of flow, promotes microbial ecosystem in full basin It develops in a healthy way;In addition, in the hemi-closure space that ecological reef surface and ecologic reef are formed, good Tibetan is provided for aquatile Body, rest, oviposition, bait space form good suitable aquatic life under the action of aerator, aerobic microbiological The environment of object breeding, gradually forms the perfect food comprising microorganism, zoobenthos, zooplankter, fish, water plant etc. Catenary system, the structure of gradual perfection water ecosystem.
Ecologic reef, can also be by microorganism to water nutrition, organic matter etc. while immobilized breeding microorganism Sorption enhanced is decomposed, to adjust oxidation-reduction potential, the water pH value of water body and bed mud water termination, and by changing bubble Climbing speed adjusts water body fluidised form, reaches the regulation and control to the water ecology factor;The lake and reservoir river basin ecological factor and gene expression are received For rice adjusting device by understanding water quality situation of change in real time to water quality monitoring, real-time monitoring water body fluidised form, dissolved oxygen are dense Microorganisms in water can be changed in the ecological factors such as degree, water body oxidation-reduction potential, pH value while improving the water ecology factor Gene expression, make microorganism can adapt to water body environment variation, to keep microorganism permanently effective to water nutrition, Organic matter etc. carries out decomposition sorption enhanced.
In the more basin of sludge content, the release of nutritive salt is to cause basin water body regulation effect inapparent in sludge Major reason, therefore, sludge reducing high-efficiency biochemical treatment device is used in combination in the more water body of sludge content can be significantly Water body treating effect is improved, and sludge reducing high-efficiency biochemical treatment device is high to the removal effect of sludge, sewage is sought after processing Support salt content it is low can direct emission enter in basin, then via the decomposition sorption enhanced of aerobic microbiological in basin, two will not be caused Secondary pollution.Nanometer oxygen-dissolving apparatus, microbubble and micro-nano disperser and ecologic reef etc. reach jointly to water pollution in pool The efficient removal of object realizes that the total amount of pollutant is cut down in water body and bed mud, meanwhile, it reduces water body organism and deposits in bed mud, Reach ecological dredging effect, in conjunction with sludge reducing high-efficiency biochemical treatment device to having the trans-utilization of sludge, makes basin It is interior long-term without carrying out dredging, save the dredging cost of great number.
In side slope reparation, prevent the soil in side slope from entering water body under rainwash by being laid with ecological revetment brick And bring a large amount of nutriment in soil into water body, plant upper water-fast one side of wet plant in ecological revetment brick planting intracavitary Face can have better fixed function, another aspect plant that can retain rainwater with side slope soil, mitigate rainwater and rushed to soil Brush reduces the external source pollution of water body, and the water body to realize side slope is firm and reduces the pollution of water body external source, in addition, plantation Water-fast wet plant is also the chief component for the plant ecosystem for building watershed ecosystem.
In shoal, ecologic reef and adding for microorganism can quickly build microbial ecosystem, also be given birth to for animal State system provides good basis, then establishes animal ecology system faster by launching certain local aquatic animal;Water Matter purification basket accelerates the structure of microbial ecosystem while building plant ecosystem by sorbing material;It sprays in shoal Nutritive salt, plant can be provided for the growth of purification of water quality basket implants and microorganism and ecological brick implants by spilling biological purification system Fast-growth breeding with microorganism can provide bait and good rest and oviposition production institute for aquatic animal, promote entire ecology The health of system is quickly built.
It is applied in basin in existing pool shoal or the pool shoal rebuild by the above equipment and technology, The pollutant of original pool can be effectively prevent to accumulate and discharge, change pool anaerobic conditions, improve sediment pollution situation, promoted whole The growth and breeding of a basin aerobic microbiological, it is ensured that microorganism full basin is realized to water pollution by the sorption enhanced of nutritive salt The reduction of object total amount realizes that the water and soil of side slope is firm and reduces external source pollution, the benign ecosystem in full basin is promoted to build.

Claims (6)

1. the method for a kind of basin pool shoal molecular fluid restoration of the ecosystem, mainly by pool(1), side slope(4)The shoal and(2)Three Part restorative procedure composition is first chosen according to the following conditions before implementing pool shoal restoration of the ecosystem:
Condition 1:It whether there is pool in basin(1);
Condition 2:It whether there is shoal in basin(2);
If pool is not present in basin(1)Just by excavating pool(1)Or the engineering measure of groynes is built to form pool region; If shoal is not present in basin(2)Just by excavating pool(1)The earthwork landfill reduce basin channel gradient or build submerged breakwater Engineering measure form shoal(2)Region, it is characterized in that the pool(1)The total amount of pollutant in reparation is cut down, mainly It is to be realized in basin by high dissolved oxygen technology, microorganism resolution technology, ecological factor control technique and sludge reduction technology Sludge reduction;The side slope(4)Water and soil in reparation is firm, mainly by being laid with ecological revetment brick and planting water-fast wet Plant is firm to realize side slope water and soil;The shoal(2)Ecosystem structure in reparation, mainly by building plant The ecosystem builds microbial ecosystem and structure animal ecology system to realize the structure of the ecosystem.
2. the method for a kind of basin pool shoal according to claim 1 molecular fluid restoration of the ecosystem, it is characterized in that described Pool(1)High dissolved oxygen technology in reparation is mainly by nanometer oxygen-dissolving apparatus(16), high dissolved oxygen generating device(11), high dissolved oxygen hair Generating apparatus(11)To authorize the device being related in patent of invention ZL 201110455752.3, microbubble and the diffusion of micro-nano bubble Device(18), microbubble and micro-nano bubble diffusing apparatus(18)It is related to authorize in patent of invention ZL 201110180368.7 Device realize;Microorganism resolution technology is added by microorganism and with the ecologic reef for adjusting ecological factor function(19), tool There is the ecologic reef for adjusting ecological factor function(19)To authorize the content being related in utility model patent ZL 201620993812.5 To realize;Ecological factor control technique is by ecological factor and gene expression nanometer adjusting device(24), ecological factor and gene table Up to nanometer adjusting device(24)For authorize in patent of invention ZL 201510010303.6 device that is related to and with adjust ecology because The ecologic reef of subfunction(19)To realize;Sludge reduction technology is by sludge reducing high-efficiency biochemical treatment device(13), sludge Minimizing high-efficiency biochemical treatment device(13)It is realized to authorize in patent of invention ZL 201110455813.6 device that is related to.
3. the method for a kind of basin pool shoal according to claim 2 molecular fluid restoration of the ecosystem, it is characterized in that described High dissolved oxygen generating device(11)For ground installation, ultramicro air bubble dissolved oxygen outlet pipe(12)With underwater nanometer oxygen-dissolving apparatus(16)'s Air inlet pipe(17)It is connected, nanometer oxygen-dissolving apparatus(16)Quantity be 3 or 3 or more, nanometer oxygen-dissolving apparatus(16)Cloth dot shape For triangle or polygon, microbubble and micro-nano bubble diffusing apparatus(18)Mounted on nanometer oxygen-dissolving apparatus(16)It is layouted The centre of shape;Ground microbiological tames culture pond(23)Interior microorganism in situ is added to adjusting ecological factor function Ecologic reef(19)Interior microorganism adds pipe(21)It is released again via Microbiological release hole afterwards(22)It puts into water body;Ecological factor and Gene expression nanometer adjusting device(24)Interior tracheae(25)With the ecologic reef with adjusting ecological factor function(19)Appendix (21)Connection;Adopt mud pipe(26)Nozzle stretches into bed mud, adopts mud pipe(26)With suction pump(15)With sludge reducing high-efficiency biochemistry Processing unit(13)Interior biological fluidized bed(14)Connection.
4. the method for a kind of basin pool shoal according to claim 1 molecular fluid restoration of the ecosystem, it is characterized in that described Side slope(4)It repairs mainly by being laid with ecological revetment brick in side slope(8), ecological revetment brick(8)For application number: 201810314574.4 the brick body being inside related to and being planted in ecological revetment brick(8)The water-fast wet plant of planting intracavitary comes real It is existing.
5. the method for a kind of basin pool shoal according to claim 1 molecular fluid restoration of the ecosystem, it is characterized in that described Shoal(2)Plant ecosystem structure is mainly by purification of water quality basket in reparation(9)Implants and shoal sprinkling biological cleaning system It unites to realize;Microbial ecosystem structure mainly passes through purification of water quality basket(9)Interior sorbing material(10)With with adjust ecology Because of the ecologic reef of subfunction(19)To realize;Animal ecology system structure is mainly introduced and is had by local aquatic animal species Adjust the ecologic reef of ecological factor function(19)To realize.
6. the method for a kind of basin pool shoal according to claim 5 molecular fluid restoration of the ecosystem, it is characterized in that described Shoal sprinkling biological purification system mainly by suction pump(5)Extract pool(1)Interior water body, through pipeline(6)Flow into shoal(2) Interior sandy beach area(3), sandy beach area(3)Pipeline(6)It is equipped with atomization mouth(7), pool(1)Area's water body is through being atomized mouth(7)It is atomized into micro- The droplet of small particle is sprayed at sandy beach area(3)Interior purification of water quality basket(9)Implants and sorbing material(10)On, purification of water quality basket (9)Interior bottom is equipped with one layer of sorbing material(10), sorbing material(10)For zeolite or activated carbon or biologic packing material, the tool in shoal There is the ecologic reef for adjusting ecological factor function(19)Also with the ecological factor of pool and gene expression nanometer adjusting device(24)With Microbial acclimation culture pond(23)It is connected.
CN201810593141.7A 2018-06-11 2018-06-11 Method for ecological restoration of molecular fluid of watershed deep pool shoal Active CN108715486B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810593141.7A CN108715486B (en) 2018-06-11 2018-06-11 Method for ecological restoration of molecular fluid of watershed deep pool shoal

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810593141.7A CN108715486B (en) 2018-06-11 2018-06-11 Method for ecological restoration of molecular fluid of watershed deep pool shoal

Publications (2)

Publication Number Publication Date
CN108715486A true CN108715486A (en) 2018-10-30
CN108715486B CN108715486B (en) 2022-05-10

Family

ID=63912956

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810593141.7A Active CN108715486B (en) 2018-06-11 2018-06-11 Method for ecological restoration of molecular fluid of watershed deep pool shoal

Country Status (1)

Country Link
CN (1) CN108715486B (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110396979A (en) * 2019-08-01 2019-11-01 福建荣冠环境建设集团有限公司 A kind of ecological restoring method of city river
CN111573862A (en) * 2020-05-26 2020-08-25 华川技术有限公司 Bionic shellfish device capable of efficiently and automatically purifying shoal water quality
WO2021081970A1 (en) * 2019-11-01 2021-05-06 南京森淼环保科技有限公司 Riverway sediment excitation device based on microbubble air flotation effect
CN112939377A (en) * 2021-04-16 2021-06-11 中国环境科学研究院 Ecological restoration method for lake swinging water in plain river network area
CN113651428A (en) * 2021-08-24 2021-11-16 南京朴厚生态科技有限公司 River channel ecological recovery mode of' side pool-heart beach

Citations (20)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001288731A (en) * 2000-04-04 2001-10-19 So Sekkei:Kk Structure of dam and water quality purifying method for river water
JP2005034140A (en) * 2003-07-02 2005-02-10 Nishimatsu Constr Co Ltd Environmental preservation material for water area and method for preservation
JP2008106433A (en) * 2006-10-23 2008-05-08 Penta Ocean Construction Co Ltd Tsunami disaster-prevention structure
CN102351267A (en) * 2011-06-28 2012-02-15 福州威龙环保技术有限公司 Micro bubble and micro-nano bubble diffusing apparatus
CN102398988A (en) * 2011-12-31 2012-04-04 福州威龙环保技术有限公司 Sludge reducing high-efficiency biochemical treatment device
CN102531155A (en) * 2011-12-31 2012-07-04 福州威龙环保技术有限公司 High dissolved oxygen generating device and application thereof
CN103452079A (en) * 2012-05-30 2013-12-18 中交上海航道勘察设计研究院有限公司 Construction method of river beach pool ecological purification system
CN103774608A (en) * 2014-02-24 2014-05-07 杭州固洁环保工程有限公司 Coupling technique of city watercourse dredging and sequence reestablishment from shoal to deep pool
CN104731004A (en) * 2014-01-13 2015-06-24 林映津 Ecological factor and gene expression nanometer regulating device used in lake and reservoir drainage basin
CN205530130U (en) * 2016-01-27 2016-08-31 刘璐 Chain ecological brick
CN106219763A (en) * 2016-09-06 2016-12-14 东北师范大学 The prevention and cure of pollution method that lake, a kind of river ecological revetment combines with shoal floating bed reparation
CN106430532A (en) * 2016-08-31 2017-02-22 林映津 Ecological reef with ecological factor regulating function
CN206089168U (en) * 2016-08-31 2017-04-12 林映津 Ecological reef with adjust ecological factor function
CN106592511A (en) * 2017-01-04 2017-04-26 无锡金利达生态科技股份有限公司 Rapid recovery method of natural river landscape of city
CN206428658U (en) * 2017-01-24 2017-08-22 陈泽伟 A kind of highway slope protection brick and highway slope protection
CN206486898U (en) * 2017-01-05 2017-09-12 河南裕华园林工程有限公司 A kind of slope protection ecologic brick
CN107165136A (en) * 2017-06-05 2017-09-15 云南大学 The storehouse tail counter regulation method protected for indigenous strains
CN206928246U (en) * 2017-07-12 2018-01-26 武汉市政工程设计研究院有限责任公司 A kind of self-locking channel underwater slope protection water-permeable brick
CN107956214A (en) * 2017-12-26 2018-04-24 中国电建集团贵阳勘测设计研究院有限公司 Ecological river channel and treatment method
CN207392145U (en) * 2017-10-30 2018-05-22 扬州大学 A kind of symmetrical insert-type ecological revetment brick of three-dimensional and ecological revetment

Patent Citations (20)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001288731A (en) * 2000-04-04 2001-10-19 So Sekkei:Kk Structure of dam and water quality purifying method for river water
JP2005034140A (en) * 2003-07-02 2005-02-10 Nishimatsu Constr Co Ltd Environmental preservation material for water area and method for preservation
JP2008106433A (en) * 2006-10-23 2008-05-08 Penta Ocean Construction Co Ltd Tsunami disaster-prevention structure
CN102351267A (en) * 2011-06-28 2012-02-15 福州威龙环保技术有限公司 Micro bubble and micro-nano bubble diffusing apparatus
CN102398988A (en) * 2011-12-31 2012-04-04 福州威龙环保技术有限公司 Sludge reducing high-efficiency biochemical treatment device
CN102531155A (en) * 2011-12-31 2012-07-04 福州威龙环保技术有限公司 High dissolved oxygen generating device and application thereof
CN103452079A (en) * 2012-05-30 2013-12-18 中交上海航道勘察设计研究院有限公司 Construction method of river beach pool ecological purification system
CN104731004A (en) * 2014-01-13 2015-06-24 林映津 Ecological factor and gene expression nanometer regulating device used in lake and reservoir drainage basin
CN103774608A (en) * 2014-02-24 2014-05-07 杭州固洁环保工程有限公司 Coupling technique of city watercourse dredging and sequence reestablishment from shoal to deep pool
CN205530130U (en) * 2016-01-27 2016-08-31 刘璐 Chain ecological brick
CN206089168U (en) * 2016-08-31 2017-04-12 林映津 Ecological reef with adjust ecological factor function
CN106430532A (en) * 2016-08-31 2017-02-22 林映津 Ecological reef with ecological factor regulating function
CN106219763A (en) * 2016-09-06 2016-12-14 东北师范大学 The prevention and cure of pollution method that lake, a kind of river ecological revetment combines with shoal floating bed reparation
CN106592511A (en) * 2017-01-04 2017-04-26 无锡金利达生态科技股份有限公司 Rapid recovery method of natural river landscape of city
CN206486898U (en) * 2017-01-05 2017-09-12 河南裕华园林工程有限公司 A kind of slope protection ecologic brick
CN206428658U (en) * 2017-01-24 2017-08-22 陈泽伟 A kind of highway slope protection brick and highway slope protection
CN107165136A (en) * 2017-06-05 2017-09-15 云南大学 The storehouse tail counter regulation method protected for indigenous strains
CN206928246U (en) * 2017-07-12 2018-01-26 武汉市政工程设计研究院有限责任公司 A kind of self-locking channel underwater slope protection water-permeable brick
CN207392145U (en) * 2017-10-30 2018-05-22 扬州大学 A kind of symmetrical insert-type ecological revetment brick of three-dimensional and ecological revetment
CN107956214A (en) * 2017-12-26 2018-04-24 中国电建集团贵阳勘测设计研究院有限公司 Ecological river channel and treatment method

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
刘信勇等: "《北方河流生态治理模式及实践》", 31 December 2016 *
刘瑛等: "利于河溪生物栖息环境生态工程述评", 《水土保持研究》 *
向旭: "对广州市水环境治理的刍议", 《广东水利水电》 *
姚云鹏等: "生态河流构建原理与技术", 《水土保持研究》 *
水利水电泄水工程与高速水流信息网等: "《泄水工程与高速水流》", 30 September 2010, 吉林人民出版社 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110396979A (en) * 2019-08-01 2019-11-01 福建荣冠环境建设集团有限公司 A kind of ecological restoring method of city river
WO2021081970A1 (en) * 2019-11-01 2021-05-06 南京森淼环保科技有限公司 Riverway sediment excitation device based on microbubble air flotation effect
CN111573862A (en) * 2020-05-26 2020-08-25 华川技术有限公司 Bionic shellfish device capable of efficiently and automatically purifying shoal water quality
CN112939377A (en) * 2021-04-16 2021-06-11 中国环境科学研究院 Ecological restoration method for lake swinging water in plain river network area
CN113651428A (en) * 2021-08-24 2021-11-16 南京朴厚生态科技有限公司 River channel ecological recovery mode of' side pool-heart beach

Also Published As

Publication number Publication date
CN108715486B (en) 2022-05-10

Similar Documents

Publication Publication Date Title
CN105330107B (en) A kind of urban waterway water purification system and purification method
CN108715486A (en) A kind of method of basin pool shoal molecular fluid restoration of the ecosystem
CN105906173B (en) Repair method and device for treating black and odorous river water
US7163628B2 (en) Water ozonation and bioremediation system and associated methods
CN107935307B (en) River water purification system for enhancing biological decomposition through cyclic reoxygenation and implementation method
CN204324990U (en) Be applicable to the multi-stage biological filter tank-ecological pond purification system into lake landscape water body
CN102464404B (en) Method and system for remediation and treatment of polluted river water
CN203768124U (en) Ecological filter for micro-polluted water treatment
CN108128967A (en) A kind of river water body dystopy comprehensive high-efficiency processing method and system
CN108821442A (en) The black smelly broken end of one kind gushes comprehensive processing method
CN110066068A (en) A kind of city eutrophication river corridor restoration method
CN104512986A (en) Combined restoring method for eutrophic lake
CN101293684B (en) Combined stream pulling type diving buoyancy lift equipment and technique for removing nature aquifer blue algae
CN211339184U (en) Domestic sewage integrated treatment equipment based on steel slag ceramsite filler biological filter
CN105236687A (en) Sewage treatment device and method for self-cleaning type micro-aeration vertical baffled wetland
CN109626595B (en) Water quality purifying microorganism ecological unit, water quality purifying microorganism ecological system and method thereof
CN102092889B (en) Method for lake purification and water ecological environmental renovation
CN215249860U (en) Purification treatment system of tail water of sewage plant
CN216039071U (en) Circulating water supply system for lakes
CN112759181B (en) Novel black and odorous river water endogenous treatment method
CN205676333U (en) A kind of system utilizing artificial wetland treatment slaughterhouse sewage
CN104016546A (en) Environment-friendly artificial wetland system for purifying dredging remained water/tail water
CN212741056U (en) High PT water body treatment system in campus pond
CN105692905B (en) A kind of land disposal method and device of ecotype landscape water body
WO2016098711A1 (en) Purification system, purification method using same, algal-proliferation controlling method, water-flow generation device, and purification device

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
GR01 Patent grant
GR01 Patent grant