CN203033833U - Device for degrading microcystis aeruginosa by algicidal bacteria - Google Patents
Device for degrading microcystis aeruginosa by algicidal bacteria Download PDFInfo
- Publication number
- CN203033833U CN203033833U CN2013200433206U CN201320043320U CN203033833U CN 203033833 U CN203033833 U CN 203033833U CN 2013200433206 U CN2013200433206 U CN 2013200433206U CN 201320043320 U CN201320043320 U CN 201320043320U CN 203033833 U CN203033833 U CN 203033833U
- Authority
- CN
- China
- Prior art keywords
- main reaction
- bacteria
- reaction post
- microcystic aeruginosa
- microcystis aeruginosa
- 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.)
- Expired - Fee Related
Links
Images
Classifications
-
- 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
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The utility model relates to a device for degrading microcystis aeruginosa by algicidal bacteria. The device comprises a water sample tank, wherein the water sample tank is connected with a main reaction column through a rotor flow meter and a water inlet pipe; a water outlet pipe is arranged at the upper part of the main reaction column; and the main reaction column is internally provided with an aeration device and is internally filled with three layers of ceramsite with different grain diameters which are reduced from bottom to top. The device disclosed by the utility model can effectively fix the algicidal bacteria WM1 (namely Bacillus megaterium) with the efficient removing effect on the microcystis aeruginosa on fillers, and can implement rapid, safe and efficient elimination of the microcystis aeruginosa through controlling hydraulic power staying time and aeration amount.
Description
Technical field
The utility model relates to a kind of device of removing wawter bloom algae microcystic aeruginosa, can be used for the removal of microcystic aeruginosa in wawter bloom or the eutrophication water.
Background technology
Along with growth and the development of industry and agriculture of urban population, the body eutrophication problem that is caused by various discharge of wastewater becomes increasingly conspicuous, and eutrophication has in various degree appearred in some lake of China.Body eutrophication causes various harmful algaes such as a large amount of breedings such as microcystic aeruginosa, anabena, and the algae pollution disaster is on the rise.The unusual breeding growth of algae, not only havoc water landscape and aquatic ecosystem in a healthy and balanced way, and discharge the algae toxin of number of different types behind the poisonous blue-green algae cell rupture in the water body, bring very big harm for human health, hydrocoles, poultry etc.
Microcystic aeruginosa is one of modal blue-green algae of breakout of water bloom, and China Taihu Lake blue-green algae breaks out greatly in recent years, and main algae is microcystic aeruginosa.When wawter bloom is decorporated, microcystic aeruginosa dead or break after can discharge born of the same parents' intracellular toxin-Microcystin (Microsystins is called for short MCs).MCs is seven peptide monocycle hepatotoxin of a class biologically active, is than the chlorophyll stable ring compound that has two keys also, and more than 60 kind of isomer arranged.The blue-green alga bloom of 25%-70% pollutes and can produce the algae toxin in the world, wherein Microcystin (Microcystins, the algae toxin kind that MCs) be that a class frequency of occurrences is the highest, generation is maximum, toxicity is the strongest, works the mischief the most serious.
Molten algae bacterium refers to by direct or indirect mode, suppresses algal grown or cracking frustule, thereby shows the bacterium of algae effect extremely.They extensively are present among seawater, lake, mud and the city appearance water body, be an important component part of biotic population structure and function in the aquatic ecosystem, the control of algal bloom, the balance of keeping the algae bio amount are had important effect.Along with the aggravation of global body eutrophication, breaking out of harmful algae wawter bloom is increased, and the environment that it causes and economic problems paid more and more attention are sought effective wawter bloom and the red-tide control approach is imperative.Utilizing physics, chemistry and other biological method to administer under the very undesirable situation of wawter bloom, molten algae bacterium as the biology of wawter bloom and red-tide control, has caused more and more people's concern.
Summary of the invention
The purpose of this utility model provides a kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa, can also greatly improve the microcystic aeruginosa clearance by fixing molten algae bacterium, can control flooding velocity, aeration rate and hydraulic detention time, microcystic aeruginosa is fully contacted with bacterium, improve alga-killing rate.
The technical scheme that the utility model is taked is:
A kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa comprises the water sample case, and the water sample case connects the main reaction post by spinner-type flowmeter, water inlet pipe, and the top of main reaction post sets out water pipe, is provided with aerating apparatus in the main reaction post.
The pottery gravel of three layers of different-grain diameter is housed in the described main reaction post, and from bottom to top particle diameter diminishes.
Described pottery gravel particle diameter is preferably at 1-3cm.
Described aerating apparatus is the aeration head of main reaction post inner bottom part, and aeration head is connected by the outer air pump of tracheae and main reaction post, and tracheae is provided with air flowmeter, valve.
Separation and purification in advance had the molten algae bacterium of the strain WM1(Bacillus megaterium of higher removal effect to microcystic aeruginosa) pour into and the gravel that is fixed in to make pottery is in the main reaction post of filler together with the LB substratum, under the condition of 20 ℃ of room temperatures, oxygen and bacteria culture medium abundance, reaction through two weeks is completely fixed on filler this molten algae bacterium, the aqueous sample stream that contains the verdigris Microcystis aeruginosa is then crossed reactor, can with filler on molten algae bacterial film fully contact, thereby reach purpose with algae removal.
Advantage of the present utility model is:
The pottery gravel is as the medium that depends on of a kind of bacterium, can farthest the molten algae bacterium WM1 that microcystic aeruginosa is had the efficient degradation effect be fixed in the reactor, simultaneously by control hydraulic detention time and aeration rate realize to microcystic aeruginosa fast, safety and removing efficiently.This device can will have the molten algae bacterium WM1(Bacillus megaterium of efficient removal effect to microcystic aeruginosa) effectively be fixed on the filler, and by control hydraulic detention time and aeration rate realize to microcystic aeruginosa fast, safety and removing efficiently.
Description of drawings
Fig. 1 is the apparatus structure synoptic diagram of the utility model embodiment 1.
Among the figure, 1. water sample case; 2. spinner-type flowmeter; 3. water inlet pipe; 4. rising pipe; 5. main reaction post; 6. air pump; 7. valve; 8. air flowmeter; 9. aeration head; 10. diameter is the pottery gravel bed of 3cm; 11. diameter is the pottery gravel bed of 2cm; 12. diameter is the pottery gravel bed of 1cm.
Embodiment
Further specify below in conjunction with embodiment.
A kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa comprises water sample case 1, and water sample case 1 connects main reaction post 5 by spinner-type flowmeter 2, water inlet pipe 3, and the top of main reaction post 5 sets out water pipe 4, is provided with aerating apparatus in the main reaction post 5.The pottery gravel of three layers of different-grain diameter is housed in the main reaction post 5, and from bottom to top particle diameter diminishes.In the present embodiment, earlier in being the reactor of 5.5L, volume loads onto the pottery gravel filler that three layers of particle diameter are respectively 3cm, 2cm and 1cm.Aerating apparatus is the aeration head 9 of main reaction post 5 inner bottom parts, and aeration head 9 is connected with main reaction post 5 air pump 6 outward by tracheae, and tracheae is provided with air flowmeter 8, valve 7.
With the cultured molten algae bacterium bacterium liquid WM1(Bacillus megaterium of 4L) pour in the reactor together with the LB liquid medium, behind the aeration 24h, take out the 300ml supernatant liquor every day from reactor, (frustule concentration is 10 to replenish corresponding microcystic aeruginosa liquid then
6Individual/as mL), bacterium to be tamed.Can see tangible bacterial film on pottery gravel surface after two weeks, namely represent the biofilm success.Microcystic aeruginosa liquid in the water sample case enters reactor by water inlet pipe from the bottom, and hydraulic detention time is controlled by spinner-type flowmeter, is 6h, and air pump control aeration intensity is 0.15m
3/ h.The microcystic aeruginosa water sample fully contacts, reacts with the bacterial film on pottery gravel surface, and water outlet is flowed out from reaction column top.After reactive system was stable, by detecting the microcystic aeruginosa cell concn of Inlet and outlet water, the result showed that this device can be realized the clearance of microcystic aeruginosa more than 80%.
Claims (4)
1. a device that utilizes molten algae degradation by bacteria microcystic aeruginosa is characterized in that, comprises the water sample case, and the water sample case connects the main reaction post by spinner-type flowmeter, water inlet pipe, and the top of main reaction post sets out water pipe, is provided with aerating apparatus in the main reaction post.
2. a kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa according to claim 1 is characterized in that, the pottery gravel of three layers of different-grain diameter is housed in the described main reaction post, and from bottom to top particle diameter diminishes.
3. a kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa according to claim 2 is characterized in that, described pottery gravel particle diameter is at 1-3cm.
4. a kind of device that utilizes molten algae degradation by bacteria microcystic aeruginosa according to claim 1, it is characterized in that, described aerating apparatus is the aeration head of main reaction post inner bottom part, and aeration head is connected by the outer air pump of tracheae and main reaction post, and tracheae is provided with air flowmeter, valve.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2013200433206U CN203033833U (en) | 2013-01-25 | 2013-01-25 | Device for degrading microcystis aeruginosa by algicidal bacteria |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2013200433206U CN203033833U (en) | 2013-01-25 | 2013-01-25 | Device for degrading microcystis aeruginosa by algicidal bacteria |
Publications (1)
Publication Number | Publication Date |
---|---|
CN203033833U true CN203033833U (en) | 2013-07-03 |
Family
ID=48685970
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2013200433206U Expired - Fee Related CN203033833U (en) | 2013-01-25 | 2013-01-25 | Device for degrading microcystis aeruginosa by algicidal bacteria |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN203033833U (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103667111A (en) * | 2013-11-07 | 2014-03-26 | 辽宁大学 | Bacillus megaterium capable of dissolving microcystis aeruginosa and application thereof |
CN104178427A (en) * | 2014-08-25 | 2014-12-03 | 云南天保桦生物资源开发有限公司 | Method for removing microcystin from spirulina |
CN111018095A (en) * | 2019-12-26 | 2020-04-17 | 中国水产科学研究院渔业机械仪器研究所 | Method for controlling cyanobacterial microcystis bloom and portable treatment system |
-
2013
- 2013-01-25 CN CN2013200433206U patent/CN203033833U/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103667111A (en) * | 2013-11-07 | 2014-03-26 | 辽宁大学 | Bacillus megaterium capable of dissolving microcystis aeruginosa and application thereof |
CN104178427A (en) * | 2014-08-25 | 2014-12-03 | 云南天保桦生物资源开发有限公司 | Method for removing microcystin from spirulina |
CN104178427B (en) * | 2014-08-25 | 2016-09-28 | 云南天保桦生物资源开发有限公司 | A kind of remove the method for Microcystin in spirulina |
CN111018095A (en) * | 2019-12-26 | 2020-04-17 | 中国水产科学研究院渔业机械仪器研究所 | Method for controlling cyanobacterial microcystis bloom and portable treatment system |
CN111018095B (en) * | 2019-12-26 | 2024-03-12 | 中国水产科学研究院渔业机械仪器研究所 | Method for controlling cyanobacteria microcystis bloom and portable treatment system |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN103112996B (en) | Aquaculture water circulation purification method and device | |
AU2012358806B2 (en) | Systems and methods for contaminant removal from a microalgae culture | |
CN101475288A (en) | Water circulation filtering system for aquiculture | |
NZ528628A (en) | Periphyton filtration pre- and post-treatment system and method | |
CN105494225A (en) | Indoor recirculating aquaculture system | |
CN108128967A (en) | A kind of river water body dystopy comprehensive high-efficiency processing method and system | |
CN203033833U (en) | Device for degrading microcystis aeruginosa by algicidal bacteria | |
KR101065814B1 (en) | Natural purification marsh | |
CN201733721U (en) | Economic water-circulating aquaculture system | |
CN203360086U (en) | Ozone gas-liquid exchange device and water purification and disinfection device applying same | |
CN205018094U (en) | Aquaculture system | |
CN104731004B (en) | The ecological factor in Hu Ku basins and gene expression nanometer adjusting device | |
CN104115781A (en) | Purification device for circulating water of aquarium | |
CN104926027A (en) | Recycling method of water for seedling culture in fresh water | |
CN102531277A (en) | Purification method and device of cold-water fish cultivation water body in mountain gully watershed | |
CN2692998Y (en) | Disposal system for cleaning circulating water of abalone breeding | |
CN102502972B (en) | Method using downflow biological aerated filter to treat algal slurry press filtrate | |
CN111995193A (en) | Integrated intelligent device and method for advanced treatment of medical wastewater | |
CN114455774B (en) | Ecological safety flocculant water transparency improving method | |
CN102491612A (en) | Device and treatment method for digesting sludge with microorganism and microfauna | |
CN106746190B (en) | Multi-carrier biological ammonia nitrogen and turbidity removal equipment for drinking water and treatment method thereof | |
CN110563150A (en) | Biological algae removal method based on proliferation of microorganisms and zooplankton | |
CN108623087B (en) | Process for treating bad water body and deep water culture | |
CN205305742U (en) | Indoor circulation recirculating aquaculture system | |
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 |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C17 | Cessation of patent right | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20130703 Termination date: 20140125 |