CN100494100C - Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide - Google Patents
Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide Download PDFInfo
- Publication number
- CN100494100C CN100494100C CNB2007100202658A CN200710020265A CN100494100C CN 100494100 C CN100494100 C CN 100494100C CN B2007100202658 A CNB2007100202658 A CN B2007100202658A CN 200710020265 A CN200710020265 A CN 200710020265A CN 100494100 C CN100494100 C CN 100494100C
- Authority
- CN
- China
- Prior art keywords
- strong
- magnetic
- algae
- flocculation
- 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.)
- Expired - Fee Related
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a method of algae bloom through strong flocculate magnetic polymers and algaecide, which comprises the following steps: using strong flocculate nature of polyaluminium chloride ferric; mixing with hyper pure magnet power; getting magnetic strong flocculant suspension; putting into water body environment with rich of algae, nitrogen and phosphor; flocculating algae cell quickly; absorbing nitrogen and phosphor; forming big block dense flocculate body; using magnetic response property of super pure magnetic iron ore power; enriching algae cell under the function of foreign field; transporting out of water body area.
Description
Technical field
The invention belongs to field of environment protection, specifically is method and algicide that a kind of flocculation magnetic polymer is administered algal tufa.
Background technology
In recent years, the generation of the rivers,lakes and seas wawter bloom of China, development have caused the extensive concern of various circles of society, large-area algal bloom, havoc the balance and stability of aquatic ecosystem, not only influenced water landscape, influenced the development of culture fishery, and algae toxicity has constituted the threat to environment for human survival.Only red tide reaches more than billions of units for the coastal financial loss that causes every year, so breaking out of algae becomes a kind of disaster.Cause that main nutrient elements that algal tufa breaks out is that nitrogen, phosphorus, particularly phosphorus in the water body plays critical effect.Remove the algal bloom method than popular at present and roughly can be summed up as physics method, chemical method and biological process.
Physics method physical method is (as high pressure ionization, high-voltage pulse, alternating intense magnetic field, ultraviolet ray, ultrasonic wave etc.) then be to be converted into chemical energy with electric energy, change molecular structure and the character enter water body or water body material, reach and kill and wound, kill impurity in algae and decomposition, the adsorbed water body, reach the purpose that purifies water system.This advantage is not destroyed water body, noresidue, but physics to kill and wound be relation of equal quantity, it is big more to kill and wound life entity, consumption is many more, it is many more to kill and wound many more energy consumptions, water quality impurity is many more, it is many more to consume energy.The method that comprises mechanical process in addition or manually salvage algae and take to dredge, the former can only can not tackle the problem at its root as easy supplementary means, and expends a large amount of manpower and materials, has little effect.
Chemical method mainly is to adopt various chemical algae removing agent, its most pronounced effects, but also have most danger, thus very prudent when using, in strict accordance with the consumption operation that requires, otherwise can cause serious consequence.Because the chemical ingredients of these algicide is the copper compound of processable, perhaps chelated copper class material, these compounds produce injury to a certain degree even cause death the Shui nationality such as fish pasture and water are biological, and carcinogenesis is arranged, and also can produce other some uncertain bad sequela.
Biological process biological restoration algicide is at tens kinds of living microorganisms and the corresponding enzyme of handling eutrophication water, it is a kind of pure biotechnological formulation of All Pure Nature, the hydrobiont in the water body and the mankind etc. are not produced any harm and side effect, in a single day product drops into water body, the algae competition nutrition source in rapid activation of the microorganism in the product and the water, thus make algae lack nutrition death, sink under water, increasing microorganism continues the dead algae of degraded, until elimination, makes water body become clear.But biological process particularly the method for restoration of the ecosystem among a small circle, the control of algal tufa is an important method in the FX. but these class methods often need to drop in advance huge artificial engineering, to create and control suppresses the condition of required waterplant of algal tufa (bottom low in transparency as submerged plant or that lack suitable bed mud is difficult to existence) or animal survival, thereby take effect slow, cost is high, the difficult improvement that generally is applicable to big area, sudden algal tufa.
Above several method, though can play the effect of alleviation to a certain extent to wawter bloom, they have, and a common shortcoming---phosphor-removing effect is not obvious, can not solve the key issue that algal tufa breaks out, and cures the symptoms, not the disease.
Once invented a kind of algae-removing method quick and with low cost of collecting at this problem application, this technology is the adsorption-flocculation algae effectively, simultaneously can rapidly algae be shifted out water body by the effect of foreign field again, and to nitrogen, phosphorus removal effect highly significant in the water body, can accomplish to treat both principal and secondary aspect of disease, but this method flocculation is quick inadequately, and the flco of formation is closely knit inadequately, is unfavorable for that follow-up magnetic mask work carries out.
Summary of the invention
The applicant has proposed a kind of method and algicide of new treating algae bloom by strong-flocculation magnetic polymer on the basis of original research work, this method not only cost is low, and has strong flocculence and fast-response, satisfies the time needs of magnetic mask work.
Technical scheme of the present invention is as follows:
The method for the treatment of algae bloom by strong-flocculation magnetic polymer, it is characterized in that it being the strong flocculence of utilizing aluminium iron polychloride, aluminium iron polychloride and ultrapure magnetic iron powder are mixed into the strong flocculation agent suspension liquid of magnetic, put in the water body environment that is rich in algae and nitrogen, phosphorus, rapid flocculation frustule and adsorption of nitrogen, phosphorus, and form the closely knit flco of bulk, utilize the magnetic responsiveness of ultrapure magnetite powder, enrichment frustule apace under the effect of outside magnetic field transports the water body zone.
The method of described treating algae bloom by strong-flocculation magnetic polymer is characterized in that by aluminium iron polychloride: the mixed of ultrapure magnetite powder: water=1-3g:0.5-1.5g:4-6ml evenly makes the strong flocculation agent suspension liquid of magnetic; Ratio in 50-200mg/L joins the strong flocculation agent suspension liquid of magnetic in the water body environment, and stirs.
The method of described treating algae bloom by strong-flocculation magnetic polymer is characterized in that by aluminium iron polychloride: the mixed of ultrapure magnetite powder: water=2g:1g:5ml evenly makes the strong flocculation agent suspension liquid of magnetic; Ratio in 70-200mg/L joins the strong flocculation agent suspension liquid of magnetic in the water body environment, stirs between 20 seconds in second to 50.
The algicide for the treatment of algae bloom by strong-flocculation magnetic polymer is characterized in that it being the aqueous suspension that contains aluminium iron polychloride and ultrapure magnetite powder.
The algicide of described treating algae bloom by strong-flocculation magnetic polymer is characterized in that wherein the proportioning of each component is aluminium iron polychloride: ultrapure magnetite powder: water=1-3g:0.5-1.5g:4-6ml.
The principle of the invention is: Yi Bian utilize the strong flocculence rapid flocculation frustule of aluminium iron polychloride and adsorption of nitrogen, phosphorus, and the closely knit flco of formation bulk, utilize the magnetic responsiveness of ultrapure magnetite powder on one side, enrichment frustule apace under the effect of outside magnetic field, transport the lake region, alleviate the pressure that the lake algal tufa causes to a certain extent.The material therefor aluminium iron polychloride is the strong flocculation material of a kind of cheapness, and scale operation easily, stable performance are easy to reclaim; Ultrapure magnetite powder source is wide, cost is low and environmental friendliness.
Advantage of the present invention:
The frustule clearance reach more than 99%, total nitrogen reduce about 85%, total phosphorus reduces more than 93%, COD reduces about 95%, turbidity and reduces more than 96%.
The flocculation of this method fast and flco closely knit, satisfy the needs of magnetic mask work.Simultaneously, the magnetic flocculant stable performance can repeat to recycle.
3. the performance magnetic breeze and the synergy of flocculation agent by force, existing strong flocculence has strong magnetic responsiveness again, makes that objectionable impuritiess such as algal tufa, nitrogen, phosphorus, COD are shifted out under the action of a magnetic field fast, has stopped secondary pollution.
Embodiment
With aluminium iron polychloride: the mixed of ultrapure magnetite powder: water=2g:1g:5ml evenly makes the strong flocculation agent suspension liquid of magnetic.Ratio in 70-200mg/L joins the strong flocculation agent suspension liquid of magnetic in the algae liquid, and normal speed stirs about 20s.Utilize the magnetic responsiveness of magnetic, objectionable impuritiess such as algae are removed down fast in the water body in the effect of outside magnetic field.
Claims (3)
1, the method for the treatment of algae bloom by strong-flocculation magnetic polymer, it is characterized in that it being the strong flocculence of utilizing aluminium iron polychloride, will be by aluminium iron polychloride: the mixed of ultrapure magnetite powder: water=1-3g:0.5-1.5g:4-6ml evenly makes the strong flocculation agent suspension liquid of magnetic, in the ratio of 50-200mg/L the strong flocculation agent suspension liquid of magnetic is put into and to be rich in algae and nitrogen, in the water body environment of phosphorus, and stir, rapid flocculation frustule and adsorption of nitrogen, phosphorus, and the closely knit flco of formation bulk, utilize the magnetic responsiveness of ultrapure magnetite powder, enrichment frustule apace under the effect of outside magnetic field transports the water body zone.
2, the method for the treatment of algae bloom by strong-flocculation magnetic polymer according to claim 1 is characterized in that by aluminium iron polychloride: the mixed of ultrapure magnetite powder: water=2g:1g:5ml evenly makes the strong flocculation agent suspension liquid of magnetic; Ratio in 70-200mg/L joins the strong flocculation agent suspension liquid of magnetic in the water body environment, stirs between 20 seconds in second to 50.
3, the algicide for the treatment of algae bloom by strong-flocculation magnetic polymer is characterized in that it being the aqueous suspension that contains aluminium iron polychloride and ultrapure magnetite powder, and the proportioning of each component is aluminium iron polychloride: ultrapure magnetite powder: water=1-3g:0.5-1.5g:4-6ml.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100202658A CN100494100C (en) | 2007-03-11 | 2007-03-11 | Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100202658A CN100494100C (en) | 2007-03-11 | 2007-03-11 | Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide |
Publications (2)
Publication Number | Publication Date |
---|---|
CN101041530A CN101041530A (en) | 2007-09-26 |
CN100494100C true CN100494100C (en) | 2009-06-03 |
Family
ID=38807354
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB2007100202658A Expired - Fee Related CN100494100C (en) | 2007-03-11 | 2007-03-11 | Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN100494100C (en) |
Families Citing this family (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100556822C (en) * | 2007-11-19 | 2009-11-04 | 中国科学院等离子体物理研究所 | The eutrophication material shifts out method and apparatus in the water body in lake |
CN101289240B (en) * | 2008-02-28 | 2011-03-16 | 中国科学院等离子体物理研究所 | Novel finishing agent for removing algal tufa and treatment method |
CN102249386B (en) * | 2011-07-11 | 2012-09-05 | 三峡大学 | Preparation method of modified kaoline alga flocculating agent and application thereof |
CN102503005B (en) * | 2011-11-10 | 2013-05-01 | 安徽雷克环保科技有限公司 | Method for replacing bottom sludge of polluted water in site and sludge cleaning equipment |
CN103030203B (en) * | 2012-12-27 | 2014-06-11 | 中国科学院合肥物质科学研究院 | Preparation method of composite inorganic polymer stable algaecide and algae removing method |
CN103255088A (en) * | 2013-04-28 | 2013-08-21 | 中国海洋石油总公司 | Magnetic flocculant and application method thereof |
CN103382523B (en) * | 2013-06-29 | 2015-10-21 | 中南大学 | A kind of precursor Preparation Method for the deironing of hydrometallurgy acid leaching solution magnetic flocculation |
CN105597637B (en) * | 2015-12-21 | 2017-06-13 | 广西壮族自治区环境保护科学研究院 | A kind of preparation method of magnetic nano particle |
CN105439388B (en) * | 2015-12-30 | 2018-06-01 | 苏州宏久航空防热材料科技有限公司 | The device and its application method of blue-green alge in a kind of removal water body |
CN107986408B (en) * | 2017-12-05 | 2021-06-01 | 湖南城市学院 | Liquid magnetic composite flocculant and preparation and application thereof |
CN110894090A (en) * | 2018-09-13 | 2020-03-20 | 湖州欧美新材料有限公司 | Algicide and application thereof |
CN110577315B (en) * | 2019-09-29 | 2021-03-23 | 中国环境科学研究院 | Whole-process treatment method for phytoplankton |
CN113210446A (en) * | 2021-06-11 | 2021-08-06 | 甘肃酒钢集团宏兴钢铁股份有限公司 | Magnetic separation descaling device, descaling system and descaling method for thin strip steel |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3697420A (en) * | 1968-03-19 | 1972-10-10 | Donald Stapf Blaisdell | Method and apparatus for treatment of aqueous liquor |
US4089779A (en) * | 1975-11-24 | 1978-05-16 | Georgia-Pacific Corporation | Clarification process |
CN1824611A (en) * | 2006-01-26 | 2006-08-30 | 中国科学院等离子体物理研究所 | Composite type inorganic polymer water quality purifier and method of magnetic gathering algae eliminating |
CN1916179A (en) * | 2006-07-28 | 2007-02-21 | 中国科学院等离子体物理研究所 | Magnetic method for preprocessing flocculation of collected object for L - lactic fermentation liquid |
CN1919745A (en) * | 2006-07-19 | 2007-02-28 | 中国科学院等离子体物理研究所 | Method of control town domestic sewage using magnetic polymers guided by fly ash and flocculant |
-
2007
- 2007-03-11 CN CNB2007100202658A patent/CN100494100C/en not_active Expired - Fee Related
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3697420A (en) * | 1968-03-19 | 1972-10-10 | Donald Stapf Blaisdell | Method and apparatus for treatment of aqueous liquor |
US4089779A (en) * | 1975-11-24 | 1978-05-16 | Georgia-Pacific Corporation | Clarification process |
CN1824611A (en) * | 2006-01-26 | 2006-08-30 | 中国科学院等离子体物理研究所 | Composite type inorganic polymer water quality purifier and method of magnetic gathering algae eliminating |
CN1919745A (en) * | 2006-07-19 | 2007-02-28 | 中国科学院等离子体物理研究所 | Method of control town domestic sewage using magnetic polymers guided by fly ash and flocculant |
CN1916179A (en) * | 2006-07-28 | 2007-02-21 | 中国科学院等离子体物理研究所 | Magnetic method for preprocessing flocculation of collected object for L - lactic fermentation liquid |
Also Published As
Publication number | Publication date |
---|---|
CN101041530A (en) | 2007-09-26 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100494100C (en) | Method for treating algae bloom by strong-flocculation magnetic polymer and algaecide | |
Yetilmezsoy et al. | Decolorization and COD reduction of UASB pretreated poultry manure wastewater by electrocoagulation process: A post-treatment study | |
Shen et al. | Enhanced algae removal by drinking water treatment of chlorination coupled with coagulation | |
Liu et al. | Applying an electric field in a built-in zero valent iron–anaerobic reactor for enhancement of sludge granulation | |
Gu et al. | Microcystis aeruginosa removal by in situ chemical oxidation using persulfate activated by Fe2+ ions | |
CN100519437C (en) | Composite type inorganic polymer water quality purifier and method of magnetic gathering algae eliminating | |
Fang et al. | Effects of metabolic uncouplers on excess sludge reduction and microbial products of activated sludge | |
Tang et al. | Role of extracellular polymeric substances and enhanced performance for biological removal of carbonaceous organic matters and ammonia from wastewater with high salinity and low nutrient concentrations | |
CN106517634B (en) | A kind of processing method of high COD with high salt difficult to degrade and high solvent content waste water | |
CN108423781A (en) | A kind of preparation method and application of magnetic flocculant | |
CN101624240A (en) | Blue algae killing method | |
CN101712504A (en) | Magnetic flocculating agent and method for clearing algal bloom by using same | |
CN108409080A (en) | A kind of in-situ sediment remediation particle and preparation method thereof, application method, application | |
CN103030203B (en) | Preparation method of composite inorganic polymer stable algaecide and algae removing method | |
Hassan et al. | Exposure effect of magnetic field on water properties in recirculation aquaculture systems (RAS) | |
Zhang et al. | Sludge predation by aquatic worms: Physicochemical characteristics of sewage sludge and implications for dewaterability | |
CN101786745A (en) | Emergent large and medium-sized natural water body algae pollution remediation technique capable of resisting light stormy waves | |
Lv et al. | Microalgae removal technology for the cold source of nuclear power plant: A review | |
Xiong et al. | Synergistic analysis of performance, microbial community, and metabolism in aerobic granular sludge under polyacrylonitrile microplastics stress | |
CN101134615B (en) | Method for treating fresh water bloom by magnetic control modified coal ash and flocculating agent | |
CN105217790A (en) | Sewage treatment systems | |
CN110577315B (en) | Whole-process treatment method for phytoplankton | |
CN101643262A (en) | Composite type magnetic trap flocculant and method for removing algaltufa by using flocculant | |
CN100500588C (en) | Preparation method for composite flocculant and method of harnessing alga bloom | |
CN108726821A (en) | A kind of heavy metal sewage sludge innocuity disposal system and method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
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: 20090603 Termination date: 20110311 |