CN103626299B - Method for cooperatively controlling microcystis aeruginosa and purifying water quality by using Plagiognathops microlepis, hyriopsis cumingii, Bellamya aeruginosa and calamus - Google Patents
Method for cooperatively controlling microcystis aeruginosa and purifying water quality by using Plagiognathops microlepis, hyriopsis cumingii, Bellamya aeruginosa and calamus Download PDFInfo
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- CN103626299B CN103626299B CN201310658764.5A CN201310658764A CN103626299B CN 103626299 B CN103626299 B CN 103626299B CN 201310658764 A CN201310658764 A CN 201310658764A CN 103626299 B CN103626299 B CN 103626299B
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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
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
The invention discloses a method for cooperatively controlling microcystis aeruginosa and purifying water quality by using Plagiognathops microlepis, hyriopsis cumingii, Bellamya aeruginosa and calamus, and belongs to the technical field of water quality purification. The method comprises the following implementation steps: 1, selecting a specific eutrophication water area; 2, putting the hyriopsis cumingii into a net bag of a continuous ecological floating bed; and 3, throwing the Plagiognathops microlepis and the Bellamya aeruginosa into the water respectively. The method is simple and practical, can control the microcystis aeruginosa on upper, middle and lower layers of the water and microcystis aeruginosa hypopus in bottom mud and achieves an effect of purifying the water quality; various types of organisms are added, so the biological diversity of the water is improved and balance of a water ecological system is promoted; the hyriopsis cumingii, the Bellamya aeruginosa and the Plagiognathops microlepis are caught, so a certain economic value is achieved; and the calamus can be harvested at fixed period and can be used for feeding animals or serve as paper-making raw materials, so secondary pollution is avoided.
Description
Technical field
The invention belongs to field of water quality purification, specifically, relate to a kind of fish, two kinds of zoobenthos and a kind of emergent and combine control algae and method for purifying water, more particularly, relate to a kind of thin squama silver xenocypris, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, belong to water-treatment technology field.
Background technology
Lake is one of important water resources of China, for the mankind provide irreplaceable ecology and social service function.But China's lake eutrophication is on the rise.The most obvious feature instantiation of lake eutrophication is algae " overgrowing " and algal bloom, and therefore, the excessive algae of removing in eutrophication water is an importance in eutrophication control.Microcystic aeruginosa is the modal algae kind of algal bloom, quantity and the outburst frequency are preponderated (Gao Xueqing etc., Nutrient Energetics of Microcytis Aeruginosa is studied, Peking University's journal, 1994; Metallographic is bright, Chinese Lakes eutrophication (), (two). Chinese Lakes environment, Maritime Press, 1995).Therefore, how to control microcystic aeruginosa and become the difficult problem that vast researcher is solution lake eutrophication.In recent years, non-classical biomanipulation has been widely used in lake eutrophication improvement, and achieves good effect.As China Patent No. 200710071817.8, disclose the patent of invention that a name is called " silver carp, bighead and cladophora united algae control method ", the method of this invention is: in eutrophication water, throw in silver carp and bighead, and in water body, the input density of silver carp and bighead is 60 ~ 100g/m
3, the input ratio of silver carp and bighead is 3:1 ~ 4:1, and single cabrage amount of silver carp or bighead is 60 ~ 200g; The floating net cage that length × wide × height is of a size of 1 ~ 2m × 1 ~ 2m × 1 ~ 2m is placed, apposition growth bristle algae on net cage in eutrophic water body.This invention make use of silver carp and the bighead filter food to eutrophic water algae remove and bristle algae to the removal of water nutrition material, thus reach and control algae content in former water, reduce former water nutrition level, be beneficial to the processed conventionally object of tap water.And for example China Patent No.: 200710144842.4, disclose a name and be called a kind of patent of invention utilizing zooplankton and filter-feeding fish series connection to remove the method for algae, the method of this invention is: be together in series by least two storing facilities of waters, then algae-containing water is flow through each storing facilities of water successively, hydraulic detention time in each storing facilities of water is 1 ~ 3 day, zooplankton or filter-feeding fish is alternately put in a suitable place to breed in adjacent two storing facilities of waters, putting zooplankton in a suitable place to breed is take Microalgae as the Daphnia magna of eating, fish in the storing facilities of water of putting zooplankton in a suitable place to breed are cleared up away completely or throw in predacious fish simultaneously, the storing facilities of water stocked carp of putting filter-feeding fish in a suitable place to breed is silver carp, bighead or only put silver carp in a suitable place to breed, silver carp breeding density is 40 ~ 200g/m
3, the single tail fish of silver carp is heavily 60 ~ 500g, and bighead and silver carp breeding density are than being 1:3 ~ 1:5, and the single tail fish of bighead is heavily 60 ~ 500g.This invention effectively can remove the algae in natural water body.
But by piscine organism algae control technology educational circles exist larger dispute, on the one hand, fish excessively put the eubiosis may destroying water body in a suitable place to breed, the ecosystem of water body is damaged; On the other hand, fish can not control the blue-green algae of each water layer and N, P content reduced in water body.
Summary of the invention
the technical problem that 1, will solve
The problem of disputing on is there is for utilizing the biological microcystic aeruginosa that processes in prior art, the invention provides thin squama silver xenocypris, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, the main body fish of traditional non-classical biomanipulation is replaced with one " environment-protective fishing "-thin squama silver xenocypris by it, and the zoobenthos-hydriopsis cumingii introduced in two kinds of lakes and Bellamya sp and a kind of emergent-calamus, by coordinating the effect reaching high-efficient purification eutrophication water between this, to realizing while the comprehensive control microcystic aeruginosa of water body different depths purification of water quality.
2, technical scheme
In order to overcome the above problems, the technical solution adopted in the present invention is as follows:
Thin squama silver xenocypris, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, the steps include:
Step one: select specific eutrophic water, nitrogen, phosphorus, COD and BOD in water
5index meet following requirement: 0.7 mg/L < TN < 1.3mg/L, 0.05 mg/L < TP < 0.09 mg/L, 8 mg/L < COD < 12 mg/L, 5 mg/L < BOD
5< 8 mg/L, and full depth is no more than 3m, and the flow velocity of current is 0 ~ 0.1m/s, and in hydrobiontic algae, the mass ratio of microcystic aeruginosa is more than or equal to 50%, and the water surface being placed plantation has the biological floating bed in flakes of calamus; Described biological floating bedly in flakes comprise biological floating bed body and mesh bag; The surrounding of described biological floating bed body has supporting pile, and biological floating bed body is intersected by strip support bar and forms, and forms space between strip support bar; Also comprise bamboo basket in described space, the Four built in boundaries of bamboo basket is on the strip support bar of space surrounding; Described calamus sponge wrapping root system, plants in bamboo basket; Described mesh bag ties up on strip support bar by acrylic fibers rope; The distance that described mesh bag is dried up is 30 ~ 50cm;
Step 2: loaded in mesh bag biological floating bed in flakes by hydriopsis cumingii, the diameter of mesh bag is 20cm, the size of hydriopsis cumingii is 120g/, and it is 2 ~ 4kg/m that hydriopsis cumingii throws in density
3;
Step 3: press 200 ~ 400g/m respectively in water body
3, 1 ~ 3kg/m
3density throw in thin squama silver xenocypris and Bellamya Aeruginosa Reeve, wherein thin squama silver xenocypris list cabrage amount is 5 ~ 6g, and the single weight of Bellamya Aeruginosa Reeve is 2.5 ~ 3.5g.
Preferably, the individual plant weight of described calamus is 600g, and planting density is 9 strains/m
2.
Preferably, the injected volume of described Plagiognathops microlepis, hydriopsis cumingii, Bellamya Aeruginosa Reeve is respectively 0.3kg/m
3, 3kg/m
3with 2.5 kg/m
3.Namely the proportioning of three is 3:30:25, and this ratio can also help the eubiosis while performance optimum control algae effect.
3, beneficial effect
Compared to the prior art, the invention has the beneficial effects as follows:
(1) the present invention is by controlling the distance of dried up of mesh bag, the i.e. hanging culture height of adjusting triangle sail freshwater mussel, play hydriopsis cumingii and scrape food effect to containing the filter food effect of the filteration of upper strata water body of microcystic aeruginosa, Plagiognathops microlepis centering, lower floor's microcystic aeruginosa and Bellamya Aeruginosa Reeve to bottom microcystic aeruginosa hypopus and organic debris, various bio-cooperation can realize the effective control to water body upper, middle and lower layer microcystic aeruginosa and bottom microcystic aeruginosa hypopus;
(2) the main body fish of traditional non-classical biomanipulation is replaced with one " environment-protective fishing "-thin squama silver xenocypris by the present invention, and introduce zoobenthos-hydriopsis cumingii common in two kinds of lakes and Bellamya Aeruginosa Reeve, add the species diversity of water body, be conducive to the balance of water ecosystem;
(3) in the present invention thin squama silver xenocypris, hydriopsis cumingii movement can scrape by Bellamya sp food, restrained effectively the increasing action of movement to water nutrition, decrease the nutrition source needed for Growth of Microcystis aeruginosa to a certain extent;
(4) be conducive to routine maintenance management by mesh bag hanging culture hydriopsis cumingii in the present invention, and easily fish for results, fish for Plagiognathops microlepis and Bellamya Aeruginosa Reeve simultaneously, there is certain economic worth;
(5) calamus that the present invention selects can utilize nutritive salt in water body preferably, has good cleaning action to water quality, and periodical reaping can nutrition purposes, especially for feeding animals or the starting material as papermaking etc. simultaneously, avoid secondary pollution;
(6) the present invention selects specific animals and plants to process specific water body, when condition all meets, can not destroy the eubiosis of water body, on the other hand, can also reduce the microcystic aeruginosa of each water layer and reduce the content of water body N, P etc.;
(7) the present invention is simple to operate, and the content of each material is reasonable in design, easy handling, is convenient to promote.
Accompanying drawing explanation
Fig. 1 is the present invention's biological floating bed in flakes structural representation used;
Fig. 2 is present system distribution schematic diagram.
In figure: 1, supporting pile; 2, calamus; 3 acrylic fibers ropes; 4, mesh bag; 5, hydriopsis cumingii; 6, thin squama silver xenocypris; 7, Bellamya Aeruginosa Reeve; 8, at the bottom of pond.
embodiment:
Below in conjunction with accompanying drawing, the specific embodiment of the present invention is elaborated.
embodiment 1
As shown in Figure 1 and Figure 2, thin squama silver xenocypris, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, the steps include:
Step one: certain waters selecting eutrophication, nitrogen, phosphorus, COD and BOD in water
5index as follows: 0.7 mg/L < TN < 0.9mg/L, 0.05 mg/L < TP < 0.06mg/L, 8 mg/L < COD < 9 mg/L, 7mg/L < BOD
5< 8 mg/L, and full depth is no more than 3m, and the flow velocity of current is 0 ~ 0.1m/s, and in hydrobiontic algae, the mass ratio of microcystic aeruginosa equals 75%, and the water surface being placed plantation has the biological floating bed in flakes of calamus 2; Biological floating bedly in flakes comprise biological floating bed body and mesh bag; The surrounding of biological floating bed body has supporting pile 1, and biological floating bed body is intersected by strip support bar and forms, and forms space between strip support bar; Also comprise bamboo basket in space, the Four built in boundaries of bamboo basket is on the strip support bar of space surrounding; Calamus 2 sponge wrapping root system, plants in bamboo basket; Mesh bag 4 ties up on strip support bar by acrylic fibers rope; The individual plant weight of calamus is 600g, and planting density is 9 strains/m
2; The distance that mesh bag is dried up is 40cm;
Step 2: loaded by hydriopsis cumingii 5 in mesh bag 4 biological floating bed in flakes, the diameter of mesh bag 4 is 20cm, and the size of hydriopsis cumingii 5 is 120g/, and it is 3kg/m that hydriopsis cumingii 5 throws in density
3;
Step 3: press 300g/m respectively in water body
3, 2.5kg/m
3density throw in thin squama silver xenocypris 6 and Bellamya Aeruginosa Reeve 7, to have at the bottom of pond 8 places movable.Wherein thin squama silver xenocypris list cabrage amount is 5 ~ 6g, and the single weight of Bellamya Aeruginosa Reeve is 2.5 ~ 3.5g.
The present embodiment utilize hydriopsis cumingii to containing the filter food effect of the filteration of upper strata water body of microcystic aeruginosa, Plagiognathops microlepis centering, lower floor's microcystic aeruginosa and Bellamya Aeruginosa Reeve to the nutrition adsorption of the food effect of scraping of bottom microcystic aeruginosa hypopus and organic debris, effect of Acorus calamus on Microcystis aeruginosa to control the microcystic aeruginosa in water body upper, middle and lower and bottom, and the root system of calamus plays cleaning action to the sorption of nutritive element to water quality, thus play and jointly control microcystic aeruginosa and water purification.The method is 70% to the clearance of microcystic aeruginosa, and chlorophyll a clearance is 80%, N, the clearance of P is 70%.
embodiment 2
With embodiment 1, difference selects the waters of certain eutrophication, nitrogen, phosphorus, COD and BOD in water
5index as follows: 1.2 mg/L < TN < 1.3mg/L, 0.06 mg/L < TP < 0.07 mg/L, 9mg/L < COD < 10 mg/L, 5 mg/L < BOD
5< 6 mg/L, and full depth is 2.5m, and the flow velocity of current is 0.05m/s, and in hydrobiontic algae, the mass ratio of microcystic aeruginosa equals 50%; The distance that mesh bag is dried up is 30cm; It is 2kg/m that hydriopsis cumingii throws in density
3; The input density of thin squama silver xenocypris and Bellamya Aeruginosa Reeve is respectively 200g/m
3, 1kg/m
3.Chlorophyll a clearance is 40%, N, the clearance of P is 40%.
embodiment 3
With embodiment 1, difference selects specific eutrophic water, nitrogen, phosphorus, COD and BOD in water
5index meet following requirement: 0.9mg/L < TN < 1.1mg/L, 0.08 mg/L < TP < 0.09 mg/L, 11 mg/L < COD < 12 mg/L, 6mg/L < BOD
5< 7mg/L, in hydrobiontic algae, the mass ratio of microcystic aeruginosa equals 63%; The distance that mesh bag is dried up is 50cm; In the present embodiment, the distance of dried up of mesh bag becomes adjustable structure, constantly regulates height like this in breeding process by workman within the scope of 30 ~ 50cm, and effect can be better.It is 4kg/m that hydriopsis cumingii throws in density
3; The input density of thin squama silver xenocypris and Bellamya Aeruginosa Reeve is respectively 300g/m
3, 3kg/m
3.Be 50% to the clearance of algae, chlorophyll a clearance is 60%, N, the clearance of P is 55%.
embodiment 4
With embodiment 1, difference selects specific eutrophic water, nitrogen, phosphorus, COD and BOD in water
5index meet following requirement: 0.7 mg/L < TN < 1.0mg/L, 0.06 mg/L < TP < 0.09 mg/L, 9mg/L < COD < 11 mg/L, 6 mg/L < BOD
5< 8 mg/L, and full depth is 2.9m, and in hydrobiontic algae, the mass ratio of microcystic aeruginosa equals 55%; The distance that mesh bag is dried up is 45cm; It is 3kg/m that hydriopsis cumingii throws in density
3; The input density of thin squama silver xenocypris and Bellamya Aeruginosa Reeve is respectively 400g/m
3, 2.5kg/m
3.Be 70% to the clearance of algae, chlorophyll a clearance is 73%, N, the clearance of P is 63%.
Claims (3)
1. thin squama silver xenocypris, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and a method for purifying water, the steps include:
Step one: select specific eutrophic water, nitrogen, phosphorus, COD and BOD in water
5index meet following requirement: 0.7 mg/L < TN < 1.3mg/L, 0.05 mg/L < TP < 0.09 mg/L, 8 mg/L < COD < 12 mg/L, 5 mg/L < BOD
5< 8 mg/L, and full depth is no more than 3m, and the flow velocity of current is 0 ~ 0.1m/s, and in hydrobiontic algae, the mass ratio of microcystic aeruginosa is more than or equal to 50%, and the water surface being placed plantation has the biological floating bed in flakes of calamus; Described biological floating bedly in flakes comprise biological floating bed body and mesh bag; The surrounding of described biological floating bed body has supporting pile, and biological floating bed body is intersected by strip support bar and forms, and forms space between strip support bar; Also comprise bamboo basket in described space, the Four built in boundaries of bamboo basket is on the strip support bar of space surrounding; Described calamus sponge wrapping root system, plants in bamboo basket; Described mesh bag ties up on strip support bar by acrylic fibers rope; The distance that described mesh bag is dried up is 30 ~ 50cm;
Step 2: loaded in mesh bag biological floating bed in flakes by hydriopsis cumingii, the diameter of mesh bag is 20cm, the size of hydriopsis cumingii is 120g/, and it is 2 ~ 4kg/m that hydriopsis cumingii throws in density
3;
Step 3: press 200 ~ 400g/m respectively in water body
3, 1 ~ 3kg/m
3density throw in thin squama silver xenocypris and Bellamya Aeruginosa Reeve, wherein thin squama silver xenocypris list cabrage amount is 5 ~ 6g, and the single weight of Bellamya Aeruginosa Reeve is 2.5 ~ 3.5g.
2. thin squama silver xenocypris according to claim 1, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, is characterized in that: the individual plant weight of described calamus is 600g, and planting density is 9 strains/m
2.
3. thin squama silver xenocypris according to claim 1 and 2, hydriopsis cumingii, Bellamya Aeruginosa Reeve, calamus Collaborative Control microcystic aeruginosa and method for purifying water, is characterized in that: the injected volume of described Plagiognathops microlepis, hydriopsis cumingii, Bellamya Aeruginosa Reeve is respectively 0.3kg/m
3, 3kg/m
3with 2.5 kg/m
3.
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| CN106565011A (en) * | 2016-09-22 | 2017-04-19 | 中南大学 | Method and system for treating Microcystin-containing algae organic wastewater |
| CN112624344B (en) * | 2020-11-25 | 2022-11-04 | 安徽水韵环保股份有限公司 | Clam and snail cooperative purification system for water environment treatment |
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| JP5319190B2 (en) * | 2008-07-16 | 2013-10-16 | 三井造船株式会社 | Floating pier with water quality improvement function |
| CN101962227B (en) * | 2009-07-23 | 2012-09-05 | 上海海洋大学 | Method for removing water eutrophication |
| CN103130377A (en) * | 2011-11-25 | 2013-06-05 | 钟宇驰 | Ecological control and bioremediation coupling technology of water area pollution sources |
| CN203112596U (en) * | 2013-03-29 | 2013-08-07 | 环境保护部南京环境科学研究所 | Multifunctional biological floating bed with multiple-single floating bed connection |
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