CN107055753A - A kind of method and device of bioremediation of waters - Google Patents
A kind of method and device of bioremediation of waters Download PDFInfo
- Publication number
- CN107055753A CN107055753A CN201710317496.9A CN201710317496A CN107055753A CN 107055753 A CN107055753 A CN 107055753A CN 201710317496 A CN201710317496 A CN 201710317496A CN 107055753 A CN107055753 A CN 107055753A
- Authority
- CN
- China
- Prior art keywords
- aeration
- bioremediation
- waters
- water
- water body
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
- C02F3/348—Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/105—Phosphorus compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Microbiology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The present invention relates to a kind of method and device of bioremediation of waters.The bioremediation of waters device includes micro-pore aeration aeration system, carbon fibre ecological matrix, complex microorganism generating means, ciculation fluidized activation rinse-system and casing;The micro-pore aeration aeration system is made up of whirlpool air blower, porous tubular aerator or aeration oxygen replenishing lattice and micropore aeration pipe;Casing is divided into 4 regions and is disposed with porous tubular aerator or aeration oxygen replenishing lattice from bottom to top, carbon fibre ecological matrix, complex microorganism generating means, and ciculation fluidized activation rinse-system.Bioremediation of waters device of the present invention can be placed on river gush or lake pollution water body in, absorb water that to carry out black and odorous water biological prosthetic naturally using water (flow) direction is aerated;Or be put in land on the bank using pumping enter black and odorous water carry out it is biological prosthetic.
Description
Technical field
The present invention relates to a kind of method and device of bioremediation of waters.
Background technology
With the fast development of social economy, substantial amounts of trade effluent, sanitary sewage, the discharge of rural sewage are produced, greatly
Various pollutants in terms of gas sedimentation, precipitation runoff are flowed into be polluted in water body.Gush nitrogen phosphorus and heavy metal mistake in lake in river
Amount causes algal bloom, and the original ecological balance of water body and structure are destroyed.In recent years in the inland and coastal waters of China
Water ecology calamity caused by the blue-green algae disaster taken place frequently in water body, the body eutrophication exactly caused because of pollutant emission
Evil.The result is that cause water quality deterioration, water body black smelly, dissolved oxygen exhaust, transparency reduction, fish it is dead, to people and dynamic
Produce toxigenicity, has formed very serious problem of environmental pollution.
The Chinese patent application of Application No. 201010539843.0 discloses a kind of contaminated river water
Method and system, the Chinese patent application of Application No. 201310006749.2 disclose a kind of polluted-water governing system and its
Construction method, the method disclosed in the two patent applications is all that the reply water pollution of conventional sewage processing method is administered, work
Amount is big, efficiency is low, input is big.
The content of the invention
In place of shortcoming and defect to solve prior art, primary and foremost purpose of the invention is to provide a kind of aqueous bio strong
Change the device repaired, it is quick to improve Water microbial ecology environment.The device is gushed suitable for river, lake black and odorous water is repaired, supported
The oxygenation activation of water body is grown, is also suitable for Industrial Waste Water Treatments and town domestic sewage oxygenation aeration, river course, lake water quality, which improve, to expose
Gas etc..
Another object of the present invention is to provide a kind of method of bioremediation of waters.This method passes through micro-pore aeration oxygenation
In system, carbon fibre ecological matrix, the high-biomass biofilter of complex microorganism generating means composition, quick increase water body
Dissolved oxygen content, forms high biomass, and agitation river gushes lake-bottom settled sludge, organic pollution etc., quickly carries out organic matter
The effect such as degraded, nitrification, ammonification, improve Water quality, and then limit and eliminate the environmental condition of blue-green algae excessive proliferation, reach
Improve and repair the effect of water ecology, self purification function of water body is recovered.
The object of the invention is achieved through the following technical solutions:
A kind of bioremediation of waters device, including micro-pore aeration aeration system, carbon fibre ecological matrix, complex microorganism hair
Generating apparatus, ciculation fluidized activation rinse-system and casing;The micro-pore aeration aeration system is by whirlpool air blower, porous tubular
Aerator or aeration oxygen replenishing lattice and micropore aeration pipe composition;Casing is divided into 4 regions and is disposed with micro- from bottom to top
Hole tube aerator or aeration oxygen replenishing lattice, carbon fibre ecological matrix, complex microorganism generating means, and ciculation fluidized activation
Rinse-system;Wherein whirlpool air blower be arranged on outside casing and with porous tubular aerator or aeration oxygen replenishing lattice, Yi Jiwei
Hole aeration tube connection, micropore aeration pipe is arranged on complex microorganism generating means region.
The micro-pore aeration aeration system is by whirlpool air blower, porous tubular aerator or an aeration oxygen replenishing lattice (lattice 10
Or be not limited to) and micropore aeration pipe composition.The porous tubular aerator iris aperture is 80~100 microns.The micropore exposes
Gas, dissolved oxygen content is controlled in 2.0~4.0mg/L.
The complex microorganism generating means is main by perforated cylinder stainless steel tube or porous sintered ceramic pipe, fine increasing
Oxygen pipe, solidification microorganism agent and filter bed composition.
The filter bed is made up of one or more of compatibilities in the filtrates such as natural zeolite, haydite and volcanic rock;The solidification
Microorganism agent is in photosynthetic bacteria, Thiobacillus, actinomyces, lactic acid bacteria, saccharomycete, bacillus, denitrifying bacteria and nitrobacteria
One or more be combined.
The carbon fibre ecological matrix specific surface area is 1000~3000m2/g.The ecological base microbe of the carbon fibre of selection
Biofilm is fast, and biomembrane is easy to fall off, stable material quality, antiacid alkali resistant, and ageing-resistant, specific surface area is huge.
The ciculation fluidized activation rinse-system includes microcirculation water pump.The work of ciculation fluidized activation rinse-system is set
With one is activation indigenous flora, acceleration water body flow, increases Dissolved Oxygen in Water content, activates water body, reduces complex microorganism
It is lost in and puts into;Two can fluidize continuous inoculation reproduction propagation flora with cycle, balance aqueous bio;Three be ciculation fluidized punching
Wash, make filtrate space unimpeded, be not easily blocked.
The bioremediation of waters device is additionally provided with floating body.Floating body is option according to service condition, is high density bubble
Foam rubber-like, adjusts height of the bioremediation of waters device in polluted-water according to the depth of water, is commonly positioned at outside casing.
Biofilter is that box house need to carry out anti-corrosion, can use the material such as Corrosion Protection of Fiber Reinforced Plastics or corrosion resistance stainless steel
Material.
The lower box is provided with polluted-water entrance, and casing top enters provided with delivery port after purification, wherein polluted-water
The position of mouth is higher than porous tubular aerator or aeration oxygen replenishing lattice, and the position of delivery port is higher than complex microorganism after purification
Device.
A kind of method of bioremediation of waters, comprises the following steps:
Staying water (i.e. polluted-water) enters bioremediation of waters device, is carried out by micro-pore aeration aeration system micro-
Hole aeration oxygen replenishing activation increase water body dissolved oxygen amount, adjusts dissolved oxygen content >=2mg/L, is preferably controlled in 2.0~4.0mg/L, makes
Organic pollution in polluted-water carries out the effect such as stabilisation degraded, ammonification, nitrification;
Water body after aeration activation flows up through carbon fiber ecological matrix, and biomembrane is formed on carbon fiber ecological matrix;It is excellent
Change indigenous microorganism flora, constantly contacted with the substrate of sewage, the activity such as absorption, mass transfer, metabolism is purified to sewage;
Water body after being handled through carbon fibre ecological matrix biofilm flows through complex microorganism generating means, will be big in polluted-water
The organic matter of molecule is converted into the organic molecule of solubility, while activating indigenous flora, profit by ciculation fluidized activation system
The nitrogen and phosphorus element in water body is carried out with microorganism effectively to adsorb, convert and degrade, suppresses algae reproduction, completes to water body
It is biological prosthetic.
Methods described controls water body pH >=7 in processing procedure, and water temperature is at 20~35 DEG C.
The principle of the invention is as follows:Eutrophication, black and odorous water swash by micro-pore aeration oxygenation activation increase water body dissolved oxygen amount
Aerobic microbiological living, the effect such as stabilisation degraded, ammonification, nitrification is carried out in the short period by the organic pollution of polluted-water.
Polluted-water enters biological prosthetic device, is activated through micro-pore aeration reoxygenation, is sent out by carbon fibre ecological matrix and complex microorganism
The organic matter of macromolecular in polluted-water, the organic molecule of solubility is converted into using ectoenzyme, through enzyme reaction by generating apparatus
Primary decompose is carried out to absorb, degrade;Ciculation fluidized activation system activates indigenous flora, accelerates the propagation of indigenous profitable strain numerous
Grow, the nitrogen and phosphorus element in water body is carried out using microorganism effectively to adsorb, convert and degrade, suppresses algae reproduction, it is biological reinforced
Self-purification of water function is repaired, recovers the ecological balance.
Compared with prior art, the present invention has advantages below and beneficial effect:
Bioremediation of waters device of the present invention can be placed on river gush or lake pollution water body in, it is natural using water (flow) direction is aerated
It is biological prosthetic that water suction carries out black and odorous water;Or be put in land on the bank using pumping enter black and odorous water carry out it is biological prosthetic.
Brief description of the drawings
Fig. 1 is bioremediation of waters apparatus structure schematic diagram of the present invention, wherein:1- polluted-water entrances, 2- porous tubulars
Aerator, 3- carbon fibre ecological matrixes, 4- complex microorganism generating means, 5- micropore aeration pipes, delivery port, 7- whirlpools after 6- purifications
Whirlpool air blower, 8- microcirculation water pumps, 9- floating bodies.
Embodiment
With reference to embodiment and accompanying drawing, the present invention is described in further detail, but embodiments of the present invention are not limited
In this.
A kind of bioremediation of waters device, as shown in figure 1, including micro-pore aeration aeration system, carbon fibre ecological matrix 3,
Complex microorganism generating means 4, ciculation fluidized activation rinse-system and casing;The micro-pore aeration aeration system is roused by whirlpool
Blower fan 7, porous tubular aerator 2 and micropore aeration pipe 5 are constituted;Casing is divided into 4 regions and is disposed with micro- from bottom to top
Hole tube aerator 2, carbon fibre ecological matrix 3, complex microorganism generating means 4, and ciculation fluidized activation rinse-system;Its
Middle whirlpool air blower 7 is arranged on outside casing and is connected with porous tubular aerator 2 and micropore aeration pipe 5, micropore aeration pipe 5
It is arranged on the region of complex microorganism generating means 4.
80~100 microns of the porous tubular aerator iris aperture.The micro-pore aeration, dissolved oxygen content control exists
2.0~4.0mg/L.
The complex microorganism generating means 4 is main by perforated cylinder stainless steel tube or porous sintered ceramic pipe, fine
Oxygen increasing tube, solidification microorganism agent and filter bed composition.
The filter bed is made up of one or more of compatibilities in the filtrates such as natural zeolite, haydite and volcanic rock;The solidification
Microorganism agent is in photosynthetic bacteria, Thiobacillus, actinomyces, lactic acid bacteria, saccharomycete, bacillus, denitrifying bacteria and nitrobacteria
One or more be combined.
The specific surface area of the carbon fibre ecological matrix 3 is 1000~3000m2/g。
The ciculation fluidized activation rinse-system includes microcirculation water pump 8.
The bioremediation of waters device is additionally provided with floating body 9.Floating body is option according to service condition, is high density bubble
Foam rubber-like, adjusts height of the bioremediation of waters device in polluted-water according to the depth of water, is commonly positioned at outside casing.
The box house need to carry out anti-corrosion, can use the material such as Corrosion Protection of Fiber Reinforced Plastics or corrosion resistance stainless steel.
The lower box is provided with polluted-water entrance 1, and casing top is provided with delivery port 6, wherein polluted-water after purification
The position of entrance is higher than porous tubular aerator or aeration oxygen replenishing lattice, and the position of delivery port is sent out higher than complex microorganism after purification
Generating apparatus.
Embodiment 1
Use 2, bioremediation of waters device described in Fig. 1, power 0.85kw, 1.2~3kg of oxygen transfer rate.Repair cultivation
Water body in fish pond, bioremediation of waters device is 1 cube volume.The pool that described device is positioned over into 5 mu of waters surface on the bank, is passed through
Pump sump, ammonia nitrogen, nitrite decline 75%, 91.7%, Dissolved Oxygen in Water content DO >=4mg/L respectively after handling 2 months.
Water pH value, ammonia nitrogen and content of nitrite are as shown in table 1 before and after the processing.The filtrate key component used in embodiment is 100
The natural zeolite of the mesh of mesh~200, solidification microorganism agent is made up of photosynthetic bacteria, nitrobacteria, lactic acid bacteria, Thiobacillus key component.
Table 1 water pH value, ammonia nitrogen and content of nitrite (unit mg/L) before and after the processing
Project | PH value | Ammonia nitrogen | Nitrite |
Before processing | 8.3 | 0.4 | 0.6 |
After being repaired through 2 months | 8.1 | 0.1 | 0.05 |
Embodiment 2
Using 2, bioremediation of waters device described in Fig. 1, power 2.2kw, 4.5~14kg of oxygen transfer rate repairs wide by 6
Rice, the black smelly rivers and canals of 500 meters of length, 0.8~1.2 meter of the depth of water, bioremediation of waters device are 4 cube volumes.After processing 1 month
Water quality transparency is more than 25cm, Dissolved Oxygen in Water content DO >=2mg/L.Water body BOD before and after the processing5、CODcr、SS、NH3-N、TN、
TP contents are as shown in table 2.The filtrate key component used in embodiment is zeolite and the volcanic rock composition of 30~80 mesh, is solidified micro-
Biological agent is made up of components such as photosynthetic bacteria, Thiobacillus, nitrobacteria, denitrifying bacteria, saccharomycete, bacillus.
The water body BOD before and after the processing of table 25、CODcr、SS、NH3- N, TN, TP content (unit mg/L)
Title | BOD5 | CODcr | SS | NH3-N | TN | TP |
Former water quality data (mg/L) | 75 | 156 | 43 | 34.8 | 44.4 | 2.6 |
Water quality data (mg/L) after being repaired through 3 months | 12.2 | 31.2 | 20 | 2.6 | 11.2 | 0.6 |
Above-described embodiment is preferably embodiment, but embodiments of the present invention are not by above-described embodiment of the invention
Limitation, other any Spirit Essences without departing from the present invention and the change made under principle, modification, replacement, combine, simplification,
Equivalent substitute mode is should be, is included within protection scope of the present invention.
Claims (10)
1. a kind of bioremediation of waters device, it is characterised in that including micro-pore aeration aeration system, carbon fibre ecological matrix, answer
Close microorganism generating means, ciculation fluidized activation rinse-system and casing;The micro-pore aeration aeration system is by whirlpool air blast
Machine, porous tubular aerator or aeration oxygen replenishing lattice and micropore aeration pipe composition;Casing is divided into 4 regions simultaneously from bottom to top
It is disposed with porous tubular aerator or aeration oxygen replenishing lattice, carbon fibre ecological matrix, complex microorganism generating means, and
Ciculation fluidized activation rinse-system;Wherein whirlpool air blower is arranged on outside casing and increased with porous tubular aerator or aeration
Oxygen lattice and micropore aeration pipe connection, micropore aeration pipe are arranged on complex microorganism generating means region.
2. a kind of bioremediation of waters device according to claim 1, it is characterised in that the porous tubular aerator film
Piece aperture is 80~100 microns.
3. a kind of bioremediation of waters device according to claim 1, it is characterised in that the complex microorganism is filled
Put main by perforated cylinder stainless steel tube or porous sintered ceramic pipe, fine oxygen increasing tube solidifies microorganism agent and filter bed composition.
4. a kind of bioremediation of waters device according to claim 3, it is characterised in that the filter bed be natural zeolite,
One or more of compatibilities composition in haydite and volcanic rock;The solidification microorganism agent is photosynthetic bacteria, Thiobacillus, actinomyces, breast
One or more in sour bacterium, saccharomycete, bacillus, denitrifying bacteria and nitrobacteria.
5. a kind of bioremediation of waters device according to claim 1, it is characterised in that the carbon fibre ecological matrix ratio
Surface area is 1000~3000m2/g。
6. a kind of bioremediation of waters device according to claim 1, it is characterised in that the ciculation fluidized activation is rinsed
System includes microcirculation water pump.
7. a kind of bioremediation of waters device according to claim 1, it is characterised in that the bioremediation of waters device
It is additionally provided with floating body.
8. a kind of bioremediation of waters device according to claim 1, it is characterised in that the lower box is provided with pollution
Water body entrance, casing top provided with delivery port after purification, wherein the position of polluted-water entrance higher than porous tubular aerator or
It is that the position of delivery port after aeration oxygen replenishing lattice, purification is higher than complex microorganism generating means.
9. a kind of method of bioremediation of waters, it is characterised in that comprise the following steps:
Staying water enters bioremediation of waters device, and carrying out micro-pore aeration oxygenation activation by micro-pore aeration aeration system increases
Add water body dissolved oxygen amount, adjusts dissolved oxygen content >=2mg/L;
Water body after aeration activation flows up through carbon fiber ecological matrix, and biomembrane is formed on carbon fiber ecological matrix;Through carbon
Water body after the processing of fiber ecological base biofilm flows through complex microorganism generating means, and the organic matter of macromolecular in water body is converted into
Soluble organic molecule, while indigenous flora is activated by ciculation fluidized activation system, using microorganism in water body
Nitrogen and phosphorus element effectively adsorb, convert and degrade, and suppresses algae reproduction, completes bioremediation of waters.
10. the method for a kind of bioremediation of waters according to claim 9, it is characterised in that methods described is treated
Water body pH >=7 are controlled in journey, water temperature is at 20~35 DEG C.
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710317496.9A CN107055753A (en) | 2017-05-08 | 2017-05-08 | A kind of method and device of bioremediation of waters |
PCT/CN2017/113881 WO2018205566A1 (en) | 2017-05-08 | 2017-11-30 | Water body bioremediation method and device |
AU2017413373A AU2017413373B2 (en) | 2017-05-08 | 2017-11-30 | Method and device for bioremediation of water body |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710317496.9A CN107055753A (en) | 2017-05-08 | 2017-05-08 | A kind of method and device of bioremediation of waters |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107055753A true CN107055753A (en) | 2017-08-18 |
Family
ID=59597550
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710317496.9A Pending CN107055753A (en) | 2017-05-08 | 2017-05-08 | A kind of method and device of bioremediation of waters |
Country Status (3)
Country | Link |
---|---|
CN (1) | CN107055753A (en) |
AU (1) | AU2017413373B2 (en) |
WO (1) | WO2018205566A1 (en) |
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107720938A (en) * | 2017-11-10 | 2018-02-23 | 美尚生态景观股份有限公司 | Multi-functional black and odorous water abatement equipment |
CN108178301A (en) * | 2018-01-02 | 2018-06-19 | 京东方科技集团股份有限公司 | A kind of denitrifying method of organic wastewater |
CN108675463A (en) * | 2018-07-13 | 2018-10-19 | 上海华励振环保科技有限公司 | A kind of functional microbial activation system |
WO2018205566A1 (en) * | 2017-05-08 | 2018-11-15 | 华南理工大学 | Water body bioremediation method and device |
CN109231495A (en) * | 2018-10-30 | 2019-01-18 | 四川中科水务科技有限公司 | A kind of control algae microorganism formulation and preparation method thereof |
CN109231458A (en) * | 2018-10-15 | 2019-01-18 | 中冶华天工程技术有限公司 | A kind of efficiently general oxidation pond of carbon fiber ecological matrix and its construction method |
CN109399809A (en) * | 2018-12-17 | 2019-03-01 | 湖北兴新河道治理有限公司 | A kind of method of pollution control of water |
CN110217897A (en) * | 2019-07-05 | 2019-09-10 | 惠州学院 | A kind of sewage-treatment plant based on composite bacteria agent |
CN111689640A (en) * | 2019-03-13 | 2020-09-22 | 北京北方宏拓环境科技有限公司 | Sewage treatment method |
CN113716818A (en) * | 2021-10-14 | 2021-11-30 | 重庆工商大学 | Aquaculture waste water wisdom circulation processing system |
CN113979599A (en) * | 2021-11-19 | 2022-01-28 | 中建三局绿色产业投资有限公司 | Multi-interface gradient treatment method for mountain land type deepwater landscape lakes and reservoirs |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111072159A (en) * | 2020-01-06 | 2020-04-28 | 宁波鑫领纳米科技有限公司 | Water-purifying microbe incubator |
CN111170569B (en) * | 2020-01-14 | 2022-04-26 | 常州大学 | Promote black smelly water treatment equipment of ecological restoration |
CN112062273B (en) * | 2020-08-06 | 2023-10-13 | 深圳市广汇源环境水务有限公司 | Carbon fiber biological treatment system and method for treating overflow sewage by adopting same |
CN113003707B (en) * | 2021-02-18 | 2022-09-09 | 华北水利水电大学 | Organic pollution river course normal position processing apparatus |
CN117125812A (en) * | 2023-09-13 | 2023-11-28 | 华北水利水电大学 | Microbial ecological restoration generating system of sludge-free aerobic tank and manufacturing method thereof |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2003006385A2 (en) * | 2001-07-09 | 2003-01-23 | Peter Langendorf | Textile material for using in a biological sewage treatment installation |
CN104671417A (en) * | 2015-02-15 | 2015-06-03 | 河北省环境科学研究院 | Novel combined bio-floating bed |
CN104817167A (en) * | 2015-04-13 | 2015-08-05 | 安徽华骐环保科技股份有限公司 | Water-level descending backwashing method for up-flow biological aerated filter |
CN205925430U (en) * | 2016-07-01 | 2017-02-08 | 广州紫科环保科技股份有限公司 | Little biological filter deodorizing device |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2518743B2 (en) * | 1991-06-24 | 1996-07-31 | 株式会社荏原製作所 | Downflow biofilter for organic wastewater |
GB201015134D0 (en) * | 2010-09-13 | 2010-10-27 | Fulford Galen Y | Surface reactor |
CN105236583A (en) * | 2015-10-28 | 2016-01-13 | 河海大学 | Lotus-root-shaped eutrophic sediment remediation system capable of aeration |
CN105399209A (en) * | 2015-11-30 | 2016-03-16 | 江苏青禾环境修复有限公司 | In-situ remediation method for water in black and odorous river |
CN105923775B (en) * | 2016-04-13 | 2017-03-08 | 中国水利水电科学研究院 | A kind of lake storehouse water environment pollution repair system |
CN205917063U (en) * | 2016-05-16 | 2017-02-01 | 华南理工大学 | Riverway water body prosthetic devices |
CN107055753A (en) * | 2017-05-08 | 2017-08-18 | 华南理工大学 | A kind of method and device of bioremediation of waters |
-
2017
- 2017-05-08 CN CN201710317496.9A patent/CN107055753A/en active Pending
- 2017-11-30 AU AU2017413373A patent/AU2017413373B2/en active Active
- 2017-11-30 WO PCT/CN2017/113881 patent/WO2018205566A1/en active Application Filing
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2003006385A2 (en) * | 2001-07-09 | 2003-01-23 | Peter Langendorf | Textile material for using in a biological sewage treatment installation |
CN104671417A (en) * | 2015-02-15 | 2015-06-03 | 河北省环境科学研究院 | Novel combined bio-floating bed |
CN104817167A (en) * | 2015-04-13 | 2015-08-05 | 安徽华骐环保科技股份有限公司 | Water-level descending backwashing method for up-flow biological aerated filter |
CN205925430U (en) * | 2016-07-01 | 2017-02-08 | 广州紫科环保科技股份有限公司 | Little biological filter deodorizing device |
Non-Patent Citations (2)
Title |
---|
杨林燕: "碳纤维复合浮床对微污染水体的净化效果研究", 《中国优秀硕士学位论文全文数据库 工程科技I辑》 * |
毛玉红: "《水生物处理新技术》", 30 April 2015, 中国铁道出版社 * |
Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2018205566A1 (en) * | 2017-05-08 | 2018-11-15 | 华南理工大学 | Water body bioremediation method and device |
CN107720938A (en) * | 2017-11-10 | 2018-02-23 | 美尚生态景观股份有限公司 | Multi-functional black and odorous water abatement equipment |
CN108178301A (en) * | 2018-01-02 | 2018-06-19 | 京东方科技集团股份有限公司 | A kind of denitrifying method of organic wastewater |
CN108675463A (en) * | 2018-07-13 | 2018-10-19 | 上海华励振环保科技有限公司 | A kind of functional microbial activation system |
CN109231458A (en) * | 2018-10-15 | 2019-01-18 | 中冶华天工程技术有限公司 | A kind of efficiently general oxidation pond of carbon fiber ecological matrix and its construction method |
CN109231495A (en) * | 2018-10-30 | 2019-01-18 | 四川中科水务科技有限公司 | A kind of control algae microorganism formulation and preparation method thereof |
CN109399809A (en) * | 2018-12-17 | 2019-03-01 | 湖北兴新河道治理有限公司 | A kind of method of pollution control of water |
CN109399809B (en) * | 2018-12-17 | 2022-10-04 | 湖北兴新生态科技有限公司 | Method for treating water pollution |
CN111689640A (en) * | 2019-03-13 | 2020-09-22 | 北京北方宏拓环境科技有限公司 | Sewage treatment method |
CN110217897A (en) * | 2019-07-05 | 2019-09-10 | 惠州学院 | A kind of sewage-treatment plant based on composite bacteria agent |
CN113716818A (en) * | 2021-10-14 | 2021-11-30 | 重庆工商大学 | Aquaculture waste water wisdom circulation processing system |
CN113979599A (en) * | 2021-11-19 | 2022-01-28 | 中建三局绿色产业投资有限公司 | Multi-interface gradient treatment method for mountain land type deepwater landscape lakes and reservoirs |
CN113979599B (en) * | 2021-11-19 | 2023-10-24 | 中建三局绿色产业投资有限公司 | Multi-interface gradient treatment method for mountain-type deepwater scenery and lake |
Also Published As
Publication number | Publication date |
---|---|
WO2018205566A1 (en) | 2018-11-15 |
AU2017413373B2 (en) | 2021-02-18 |
AU2017413373A1 (en) | 2020-01-02 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107055753A (en) | A kind of method and device of bioremediation of waters | |
CN101607760B (en) | Method form purifying polluted river | |
CN102276068B (en) | River channel ecological construction and water body restoring system | |
CN203346230U (en) | Landfill leachate treatment device | |
CN110078329A (en) | A kind of sediment in-situ is biological reinforced with benthic environment ecological restoring method | |
CN109734198B (en) | Dioxygen layer biofilm reactor for wastewater treatment and wastewater treatment method | |
CN110143737A (en) | A kind of river Ecology original position dredging restorative procedure | |
CN106115904A (en) | A kind of device and method utilizing microorganism in situ to excite quickly process black and odorous water | |
CN206188508U (en) | A treatment system for riverway water body pollutes | |
CN103319047A (en) | Landfill leachate treatment system | |
CN103183455A (en) | Device and method for biologically denitrifying wastewater with high salinity | |
CN211338974U (en) | Device for restoring black and odorous water body through local microorganism activation | |
CN103601291B (en) | A kind of method for the treatment of low carbon-nitrogen ratio sewage and denitrification filtration system | |
CN107098473B (en) | High-efficient microbial community integration denitrification device based on mineralized filler | |
CN103159317A (en) | Artificial-aeration-reinforced Land percolation water treatment device | |
CN206051664U (en) | A kind of utilization microorganism in situ excites the quick device for processing black and odorous water | |
CN104909517A (en) | Industrial production wastewater advanced treatment device | |
CN214611790U (en) | Double-group B-BAF filter tank device | |
CN106145347A (en) | A kind of restoration of the ecosystem loading pipe integrating aeration performance | |
CN214218476U (en) | Permeable reactive barrier system | |
CN205635243U (en) | Vitamin C waste water advanced treatment unit | |
CN210620557U (en) | Water body sediment repair system | |
CN210736324U (en) | Small-size river course black and odorous water processing system | |
CN113403221A (en) | Method for culturing water body purifying indigenous microorganism composite microbial inoculum | |
CN211226797U (en) | Device for purifying black and odorous water body by using combined biotechnology |
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: 20170818 |
|
RJ01 | Rejection of invention patent application after publication |