CN1858008A - Method for preventing and controlling eutrophic water bloom in drinking water source - Google Patents
Method for preventing and controlling eutrophic water bloom in drinking water source Download PDFInfo
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- CN1858008A CN1858008A CNA2006100271723A CN200610027172A CN1858008A CN 1858008 A CN1858008 A CN 1858008A CN A2006100271723 A CNA2006100271723 A CN A2006100271723A CN 200610027172 A CN200610027172 A CN 200610027172A CN 1858008 A CN1858008 A CN 1858008A
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- 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
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
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Abstract
The method of preventing and controlling eutrophic water bloom in drinking water source combines the physical shading technology and ecological float island technology and includes separating the drinking water source site into several areas, initially purifying polluted water with ecological float island to eliminate large grain suspended matter, adsorb partial nitride and phosphide and reduce wind wave; leading resource water to ecological shading area with the first ecological permeating dam and eliminating partial nitride and phosphide with the hygrophyte in the dam; eliminating harmful algae in the ecological shading area and eliminating residual nitride and phosphide with the floating aquatic plant; leading the purified water with the second ecological permeating dam to the water quality stabilizing area; and conditioning and stabilizing water quality in natural water area to obtain high quality resource water.
Description
Technical field
The present invention relates to a kind of method of preventing and treating eutrophic water bloom in drinking water source, adopt physics shading technology and ecological floating island technology, the tap water seedbed is divided into the growth that several zones purified and suppressed harmful algae,, guarantees water supply security to obtain the fine source water.Belong to water-treatment technology field.
Background technology
In recent years, the body eutrophication problem in Drinking Water in China seedbed is increasingly serious, and in two seasons of spring and summer, it is the direct disastrous result of drinking water source eutrophic that the blue-green algae algal bloom threatens water supply security.In the wawter bloom arrival, aquatic animals and plants mass mortality owing to anoxic, and then cause the water body blackout smelly, meanwhile blue-green algae also discharges the algae toxin that toxic action is only second to Dioxins, causes tap water seedbed forfeiture water supply function.In China, the water supply security problem that causes owing to the eutrophication in tap water seedbed has become the key factors of restriction society, sustainable economic development, therefore anxious guardian technique and the method for waiting to develop pointed control tap water seedbed wawter bloom.
Comparatively traditional wawter bloom method of preventing and treating is used for the improvement of small-sized landscape water body more at present, and is not suitable for the wawter bloom control on ground, drinking water source.As chemical method, add the chemical agent that has algal control, kills algae or throwing out, the problem of these class methods is that comprehensive cost is too high, and will bring potential waterhead area security risk.Publication number is that the Chinese invention patent of CN1172861 proposes " add alkaline matter and make that pH reaches 8.5～10 in the water; treating that water body leaves standstill adds acid again after the clarification and adjust to neutrality ", though adopt this method purifying water body can reach certain effect, but, will cause comprehensive destruction to whole aquatic ecosystem.It is a kind of comparatively physical method of elimination landscape water body wawter bloom commonly used that machinery is caught algae, but with regard to the wawter bloom of tap water seedbed, hazard area is huge during owing to generation, and algae is dense, so it is high to adopt this method to exist cost, remove the fatal shortcoming of inefficiency.
Hover (bed) method is that the wawter bloom that develops rapidly is is in recent years prevented and treated method, and this method is utilized floating islands such as plastic foam, directly absorbs in the water nutritive salt such as nitrogen phosphorus water surface planting humidogene and waterplant, the key factor that causes wawter bloom to take place with removal.Publication number is that the Chinese invention patent " a kind of ecology absorption view floating bed device and method that is used for treating landscape water body " of CN1644533 proposes to adopt materials such as zeolite, granulation flyash to be the absorption of floating bed matrix and enrichment water nitrogen, phosphorus, for planting the essential of growing process on floating bed, form water surface ecoscape, can constantly cut down nutritive salt level in the water simultaneously.Consideration for cost of manufacture and practicality, this fado is applied to the coastal belt of small-sized landscape water body in city and minority Hu Ku at present, but often taken place for the tap water seedbed of eutrophication in more than one hundred million cubes lake, storehouse etc. for the water yield, nitrogen, the phosphorus level of attempting to utilize relative extremely a spot of chinampa plant to remove to cut down whole water body obviously are unpractical, owing to the effect of wide natural water surface high wind wave, the chinampa also constantly exists impaired danger simultaneously; On the other hand, wawter bloom under the condition of benign climate is in case outburst, often almost be that algae just can become the dominant kind at whole waterhead area overnight, have that concentration is big, scope is wide, paroxysmal characteristics, rely on the few chinampa of relative populations this moment is impossible stop wawter bloom to spread.
It should be noted that, because the essential factor of algal grown only, some scholars propose might suppress the algal grown breeding by the physics light shading method both at home and abroad in recent years, but up to the present, because practical problemss such as the shading cost is too high, stormy waves inclement condition, technology poor operability are difficult to solve, the difficult problem that is designed to that causes corresponding waterhead area shade makes this technology still be in the experimental study stage always.
In sum, prevent and treat problem, await on the basis of existing technology, develop new comprehensive method with practical value at increasingly serious tap water seedbed wawter bloom.
Summary of the invention
The objective of the invention is at the deficiencies in the prior art, a kind of method of preventing and treating eutrophic water bloom in drinking water source is provided, can effectively eliminate the harm of algae in the water body and purify water, guarantee the water supply security in tap water seedbed, simultaneously can also keep the water ecology view, and only need cheaper running cost.
For realizing this purpose, the present invention combines physics shading technology with the ecological floating island technology, the tap water seedbed is divided into several zones, utilize the ecological floating island district that polluted water is carried out rough purification, remove the macrobead suspended matter, and remove part nitrogen, phosphorus by the effect of chinampa plant and adsorbing base, subdue stormy waves simultaneously; Utilize first step ecological permeable dam to enter ecological shading region through the source water of preliminary treatment, utilize the hygrophyte that grows on the permeable dike to remove part nitrogen, phosphorus simultaneously by the seepage effect guiding; Utilize ecological shading region to remove harmful algae in the water, utilize the floating waterplant that grows in the light screening material surface to remove residual nitrogen, phosphorus simultaneously; Utilize second stage ecological permeable dam to enter the water conditioning district by the source water of seepage effect guiding through purifying; Utilize the self-purification of natural water body in the water conditioning district source water water quality to be nursed one's health, stabilization is to obtain the fine source water, for taking the waterworks, cities and towns.
Method of the present invention specifically may further comprise the steps:
1, the tap water seedbed is divided into successively ecological floating island district, first step ecological permeable dam, ecological shading region, second stage ecological permeable dam and water conditioning district; According to day water withdrawal, region average depth and required hydraulic detention time determine described ecological floating island district, ecological shading region, the required separately water surface area in water conditioning district respectively.Wherein, the hydraulic detention time in ecological floating island district was got 0.1-1 days, and the hydraulic detention time of ecological shading region was got 7-10 days, and the hydraulic detention time in water conditioning district was got 3-5 days.
2, the ecological floating island district is made of some front and back and end to end sprawling in the ecological floating island of the water surface, utilize the ecological floating island district that contaminated water source water is carried out rough purification, remove macrobead suspended matter in the water, part nitrogen, phosphorus are removed in effect by chinampa plant and adsorbing base, subdue stormy waves simultaneously.
3, first step ecological permeable dam is made up by gravel, and dam body takes the high 0.3-0.7 rice of the daily mean water level of water, is 2-5 rice along the water (flow) direction width, plants hygrophyte on the dam; Utilize the seepage effect of first step ecological permeable dam, guiding enters ecological shading region through the source water of preliminary treatment, utilizes the hygrophyte that grows on the permeable dike to remove part nitrogen, phosphorus simultaneously.
4, ecological shading region is a light-blocking member with the sunshade net, and some sunshade nets are individually fixed in its both sides on the first step and the second stage ecological permeable dam after linking to each other, and forms the huge shading region of area; The shading rate of sunshade net is 60%-90%, to guarantee that summer, average incident intensity was lower than 3000lx; Sunshade the swimming property waterplant of charging seed on the net; Utilize ecological shading region to remove harmful algae in the water, utilize the floating waterplant that grows in the light screening material surface to remove residual nitrogen, phosphorus simultaneously.
5, second stage ecological permeable dam is made up by gravel, and dam body comes the high 0.3-0.7m of daily mean water level of water, is 2-5 rice along the water (flow) direction width, plants hygrophyte on the dam; Utilize the seepage effect of second stage ecological permeable dam, guiding enters the water conditioning district through the source water that purifies.
6, in the water conditioning district, utilize the self-purification stabilizing water quality of natural water body, after the stabilization treatment, source water reaches water supply requirement, for taking the waterworks, cities and towns.
The present invention has significant technique effect.Innovation part of the present invention is physics shading technology is combined with the ecological floating island technology, to have the ecological floating island of cutting down nitrogen phosphorus function and have the ecological light-shielding structure that significantly presses down the removing algae effect and organically make up, becoming can be at the water purification system of tap water seedbed large-scale application, the function that performance simultaneously takes stopgap measures and effects a permanent cure.The present invention also has does not need power, no power consumption, and operation is simple, and the remarkable advantage that unit construction cost, working cost and overhead charges are cheap is the tap water seedbed water protection means that meet the practical situation of China.
Description of drawings
Fig. 1 is the synoptic diagram of in the inventive method the waterhead area zoning being administered.
Among Fig. 1,1 is the ecological floating island district, and 2 is first step ecological permeable dam, and 3 is ecological shading region, and 4 is second stage ecological permeable dam, and 5 is the water conditioning district.
Embodiment
Below in conjunction with drawings and Examples technical scheme of the present invention is described in further detail.
The method that the present invention prevents and treats eutrophic water bloom in drinking water source specifically comprises following content:
1, at first, waterhead area is carried out the zone divide, as shown in Figure 1, the tap water seedbed is divided into ecological floating island district 1, first step ecological permeable dam 2, ecological shading region 3, second stage ecological permeable dam 4 and water conditioning district 5 successively.According to day water withdrawal, region average depth and required hydraulic detention time determine described ecological floating island district 1, ecological shading region 3, the required separately water surface area in water conditioning district 5 respectively.Wherein, the hydraulic detention time in ecological floating island district 1 was got 0.1-1 days, and the hydraulic detention time of ecological shading region was got 7-10 days, and the hydraulic detention time in water conditioning district was got 3-5 days.
If ecological floating island district 1, ecological shading region 3, the required separately water surface area in water conditioning district 5 are respectively S
1, S
2, S
3, according to day water withdrawal V, region average depth H
1, H
2, H
3, required hydraulic detention time is respectively T
1, T
2, T
3, then:
The total area in described ecological floating island district 1 designs as follows:
S
1＝V/(H
1×T
1)
S wherein
1Be ecological floating island district total area m
2V is a day water withdrawal m
3/ d; H is ecological floating island district average depth m; T is residence time d, gets 0.1-1d;
The total area of described ecological shading region 3 designs as follows
S
2＝V/(H
2×T
2)
S wherein
2Be ecological shading region total area m
2V is a day water withdrawal m
3/ d; H
2Be ecological shading region average depth m; T
2For residence time d, get 7-10d;
The total area in described water conditioning district designs as follows
S
3＝V/(H
3×T
3)
S wherein
2Be water conditioning district total area m
2V is a day water withdrawal m
3/ d; H
2Be water conditioning district average depth m; T
2For residence time d, get 3-5d.
2, ecological floating island district 1 is made of some front and back and end to end sprawling in the ecological floating island of the water surface, and the patent that ecological floating island is CN1644533 with reference to existing publication number is built.
Ecological floating island can be thrown in along first step ecological permeable dam 2, utilizes nylon rope and timber that ecological floating island one end is fixed on the ecological permeable dam, makes the chinampa be unlikely to float from the ecological floating island district.Utilize ecological floating island district 1, can carry out rough purification, remove macrobead suspended matter in the water, remove part nitrogen, phosphorus, can play the effect of subduing stormy waves simultaneously by the effect of chinampa plant and adsorbing base to the water at contaminated water source.
3, build first step ecological permeable dam 2, retain and cut apart water body, form ecological floating island district 1 and ecological shading region 3 respectively on first step ecological permeable dam 2 both sides.It is base material that first step ecological permeable dam 2 adopts gravels, stackablely is the bamboo cage that engineering construction is used always among the square framework of being made by bamboo, utilizes bamboo cage to be piled into permeable dike.Dam body takes the high 0.3-0.7 rice of the daily mean water level of water, is 2-5 rice along the water (flow) direction width, plants hygrophyte on the dam.Utilize the seepage effect of first step ecological permeable dam 2, guiding enters ecological shading region 3 through the source water of preliminary treatment, utilizes the hygrophyte that grows on the permeable dike to remove part nitrogen, phosphorus simultaneously.
4, ecological shading region 3 is between first step ecological permeable dam 2 and second stage ecological permeable dam 4, ecological shading region 3 is a light-blocking member with the sunshade net, after some sunshade nets link to each other, can utilize nylon rope and timber that the both sides of sunshade net are individually fixed on the first step and the second stage ecological permeable dam, form the huge shading region of area.The shading rate of sunshade net is 60%-90%, to guarantee that summer, average incident intensity was lower than 3000lx; Sunshade the swimming property waterplant of charging seed on the net is as water harmony dish, Wildcelery Herb, water lettuce etc.Utilize ecological shading region 3 can remove harmful algae in the water, utilize the floating waterplant that grows in the light screening material surface to remove residual nitrogen, phosphorus simultaneously.
5, second stage ecological permeable dam 4 is made up by gravel equally, retains and cuts apart water body, forms ecological shading region 3 and water conditioning district 5 respectively on the both sides of second stage ecological permeable dam 4.Similar with first step ecological permeable dam 2, the dam body of second stage ecological permeable dam 4 comes the high 0.3-0.7m of daily mean water level of water, is 2-5 rice along the water (flow) direction width, plantation hygrophyte such as reed, wild rice stem, cattail etc. on the dam.Utilize the seepage effect of second stage ecological permeable dam 4, guiding enters water conditioning district 5 through the source water that purifies.
6, in water conditioning district 5, any artificial structures are not set, utilize the self-purification stabilizing water quality of natural water body, through after 3-5 days the stabilization treatment, water quality can reach the source water water supply requirement.
The present invention adopts physics shading technology and ecological floating island technology, and the tap water seedbed is divided into the growth that several zones purified and suppressed harmful algae, can obtain the fine source water, guarantees water supply security.As shown in Figure 1, the contaminated water source water ecological floating island district 1 that flows through earlier, by granulation flyash, hydrated calcium silicate, the zeolite in the adsorption layer of chinampa, nitrogen, phosphorus in the direct adsorption and enrichment water of matrix such as artificial zeolite, vermiculite, the growth for the chinampa plant simultaneously provides sufficient nutrient salt; The chinampa root system of plant is that profitable strain and animalcule provide the microenvironment that is beneficial to growth and breeding, brings into play the holocoenotic water quality purification function of whole root system, impels simultaneously and comes the rapid sedimentation of macrobead suspended substance in the water, prevents the obstruction of follow-up permeable dike.
Source water through preliminary treatment is inducted into ecological shading region 3 via first step ecological permeable dam 2 by seepage effect, source water residence time in ecological shading region reached more than seven days, during this period owing to lack illumination, come the poisonous algae in the water can't growth and breeding, activity reduces greatly, sinks under water very soon and death; While is in the time of wawter bloom pilosity in summer, the shading region medial temperature can come water low more than 2 ℃ under the sunlight direct projection, the difference of regional temperature makes the water body density of shading region greater than coming water-mass density, comes water sinking in flowing thereby impel, and this has also promoted the sedimentation death of algae; The online growth of this external sunshade has a large amount of waterplant, and nitrogen, phosphorus in the water are had very strong assimilation effect, has further cut down nitrogen and phosphorous nutrient in the water.
Be inducted into water conditioning district 5 via second stage ecological permeable dam 4 by seepage effect through the source water behind the strengthened purification, in this zone, do not add any artificial-strengthening, rely on the self-purification capacity of water body itself, mainly water quality is nursed one's health and stabilization, to improve the oxygen in water level, to remove fine particulate matter by air reaeration effect, precipitating action, water microorganisms Decomposition.
Because the source water in water conditioning district 5 is constantly taken, cause the natural water in the outer ecological chinampa district 1 of first step ecological permeable dam, the water body of ecological shading region 3, and there is waterhead between the water body in water conditioning district 5, this makes source water to flow through ecological floating island district 1, ecological shading region 3 and water conditioning district 5 comparatively equably step by step by seepage effect via the adjusting of permeable dike.
Embodiment
It is water surface area 120000m that embodiment tests the place
2, average depth 8m, day service discharge 10000m
3Certain small reservoir owing to have face source, rural area sewage to enter throughout the year, serious wawter bloom phenomenon takes place in summer in this reservoir often, amount of algae is 2.7 * 10 in the water
9Individual/L, and based on deleterious microcystic aeruginosa, 0.1 meter of transparency, turbidity is 107 °, and COD is 27mg/L, and total nitrogen is 1.3mg/L, and total phosphorus is 0.3mg/L, overall water quality is the V class.For improving water quality, adopted method of the present invention.
Building height according to lineament near littoral intake is 8.5m, wide is 3m, length overall is the first step ecological permeable dam of 300m, it is base material that permeable dike adopts local gravel, stack among the square framework of making by bamboo, be the bamboo cage that engineering construction is used always, utilize bamboo cage to be piled into permeable dike.Retaining the total water surface area of water body is 13000m
2In the water body inside that is retained, it is 8.7m that the intake periphery is built height, and wide is 3m, and length overall is the second stage ecological permeable dam of 120m, forms the water district, and its water surface area is 4500m
2, plantation reed and wild rice stem on the ecological permeable dam; Throwing in by publication number along the dam outside first step ecological permeable dam is the ecological floating island of the patent design of CN1644533, and forming water surface area is 600m altogether
2The ecological floating island district; Between the first step and second stage ecological permeable dam, lay 70 long be 35m, wide is 4m, shading rate is 85% sunshade net, the formation water surface area is 9800m
2Ecological shading region, at the beginning of 4 months, spread water harmony vegetable seed and rye grass-seed toward online throwing of sunshade, to June at the beginning plant grow fine, almost be covered in whole shading region surface.
Contaminated water source current are when the ecological floating island district, and the residence time is 0.5d, go out water clarity and are promoted to 0.2m by the 0.1m before handling, turbidity drops to 63 ° by 107 ° before handling, and the algae removal rate is 7%, and the COD clearance is 14%, nitrogen removal rate is 10%, and total tp removal rate is 10%.
Treat effluent enters ecological shading region by seepage effect under the guiding of first step ecological permeable dam, the residence time is 7.8d, go out water clarity after the processing and be promoted to 1m, turbidity drops to 11 °, the algae removal rate is 91%, the COD clearance is 74%, and nitrogen removal rate is 60%, and total tp removal rate is 70%.
Source water is after second stage ecological permeable dam is guided into the water conditioning district, and amount of algae is 5.3 * 10 in the water after 3.6d time stabilization
6Individual/L, and based on harmless diatom, transparency reaches 1.3 meters, and turbidity is 9 °, and COD is 2mg/L, and total nitrogen is 0.3mg/L, and total phosphorus is 0.06mg/L, and dissolved oxygen is 9mg/L, and water quality rises to the III class, satisfies tap water seedbed water quality requirement.
Claims (1)
1, a kind of method of preventing and treating eutrophic water bloom in drinking water source is characterized in that comprising the steps:
1) the tap water seedbed is divided into successively ecological floating island district, first step ecological permeable dam, ecological shading region, second stage ecological permeable dam and water conditioning district; According to day water withdrawal, region average depth and required hydraulic detention time determine described ecological floating island district, ecological shading region, the required separately water surface area in water conditioning district respectively, wherein, the hydraulic detention time in ecological floating island district was got 0.1-1 days, the hydraulic detention time of ecological shading region was got 7-10 days, and the hydraulic detention time in water conditioning district was got 3-5 days;
2) the ecological floating island district is made of some front and back and end to end sprawling in the ecological floating island of the water surface, utilize the ecological floating island district that contaminated water source water is carried out rough purification, remove macrobead suspended matter in the water, part nitrogen, phosphorus are removed in effect by chinampa plant and adsorbing base, subdue stormy waves simultaneously;
3) first step ecological permeable dam is made up by gravel, and dam body takes the high 0.3-0.7 rice of the daily mean water level of water, is 2-5 rice along the water (flow) direction width, plants hygrophyte on the dam; Utilize the seepage effect of first step ecological permeable dam, guiding enters ecological shading region through the source water of preliminary treatment, utilizes the hygrophyte that grows on the permeable dike to remove part nitrogen, phosphorus simultaneously;
4) ecological shading region is a light-blocking member with the sunshade net, and some sunshade nets are individually fixed in its both sides on the first step and the second stage ecological permeable dam after linking to each other, and forms the huge shading region of area; The shading rate of sunshade net is 60%-90%, to guarantee that summer, average incident intensity was lower than 3000lx; Sunshade the swimming property waterplant of charging seed on the net; Utilize ecological shading region to remove harmful algae in the water, utilize the floating waterplant that grows in the light screening material surface to remove residual nitrogen, phosphorus simultaneously;
5) second stage ecological permeable dam is made up by gravel, and dam body comes the high 0.3-0.7m of daily mean water level of water, is 2-5 rice along the water (flow) direction width, plants hygrophyte on the dam; Utilize the seepage effect of second stage ecological permeable dam, guiding enters the water conditioning district through the source water that purifies;
6) in the water conditioning district, utilize the self-purification stabilizing water quality of natural water body, after the stabilization treatment, source water reaches water supply requirement.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100271723A CN100384757C (en) | 2006-06-01 | 2006-06-01 | Method for preventing and controlling eutrophic water bloom in drinking water source |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100271723A CN100384757C (en) | 2006-06-01 | 2006-06-01 | Method for preventing and controlling eutrophic water bloom in drinking water source |
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| Publication Number | Publication Date |
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| CN1858008A true CN1858008A (en) | 2006-11-08 |
| CN100384757C CN100384757C (en) | 2008-04-30 |
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ID=37296970
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2006100271723A Expired - Fee Related CN100384757C (en) | 2006-06-01 | 2006-06-01 | Method for preventing and controlling eutrophic water bloom in drinking water source |
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Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101234821B (en) * | 2008-02-21 | 2010-04-14 | 上海交通大学 | Method for treating landscape water body eutrophication pollution |
| CN102211817A (en) * | 2010-04-02 | 2011-10-12 | 中国科学院沈阳应用生态研究所 | Multistage ecological permeable dike for purifying small watershed water in mountain land |
| CN102234995A (en) * | 2010-09-27 | 2011-11-09 | 华北电力大学 | Ecological overtopping dam and construction method thereof |
| CN109896691A (en) * | 2017-12-08 | 2019-06-18 | 南京工大开元环保科技（滁州）有限公司 | Black-odor riverway ecological intercepting restorative procedure |
| CN110540299A (en) * | 2019-10-11 | 2019-12-06 | 徐魁 | Ecological chinampa with automatic sunshade function |
| CN110937691A (en) * | 2019-12-04 | 2020-03-31 | 珠江水利委员会珠江水利科学研究院 | Physical-biological eutrophic water bloom treatment method suitable for deep water reservoir |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN2583080Y (en) * | 2002-11-14 | 2003-10-29 | 华中科技大学 | UV controlling device for preventing 'water bloom' and 'red tide' |
| CN1546399A (en) * | 2003-12-11 | 2004-11-17 | 中国科学院水生生物研究所 | Device for inhibiting propagation of algaes |
| JP2006075089A (en) * | 2004-09-09 | 2006-03-23 | Shiga Pref Gov | Method for producing plant increased in nitrogen absorptivity and use thereof |
| CN1296294C (en) * | 2004-10-10 | 2007-01-24 | 武汉大学 | Method for removing nutrient salt in water |
-
2006
- 2006-06-01 CN CNB2006100271723A patent/CN100384757C/en not_active Expired - Fee Related
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101234821B (en) * | 2008-02-21 | 2010-04-14 | 上海交通大学 | Method for treating landscape water body eutrophication pollution |
| CN102211817A (en) * | 2010-04-02 | 2011-10-12 | 中国科学院沈阳应用生态研究所 | Multistage ecological permeable dike for purifying small watershed water in mountain land |
| CN102234995A (en) * | 2010-09-27 | 2011-11-09 | 华北电力大学 | Ecological overtopping dam and construction method thereof |
| CN102234995B (en) * | 2010-09-27 | 2014-03-19 | 华北电力大学 | Ecological overtopping dam and construction method thereof |
| CN109896691A (en) * | 2017-12-08 | 2019-06-18 | 南京工大开元环保科技（滁州）有限公司 | Black-odor riverway ecological intercepting restorative procedure |
| CN110540299A (en) * | 2019-10-11 | 2019-12-06 | 徐魁 | Ecological chinampa with automatic sunshade function |
| CN110540299B (en) * | 2019-10-11 | 2022-04-22 | 深圳市方向生态发展有限公司 | Ecological chinampa with automatic sunshade function |
| CN110937691A (en) * | 2019-12-04 | 2020-03-31 | 珠江水利委员会珠江水利科学研究院 | Physical-biological eutrophic water bloom treatment method suitable for deep water reservoir |
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| Publication number | Publication date |
|---|---|
| CN100384757C (en) | 2008-04-30 |
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