CN214654263U - Unmanned ecological active water algae control equipment - Google Patents

Abstract

The utility model discloses an unmanned ecological active water accuse algae equipment, including the hull, be provided with high-pressure pump, reaction cavity and high-pressure agitator on the hull, the water inlet of high-pressure pump is connected with the pipe that absorbs water, and the delivery port of high-pressure pump is connected with the shower, and the high-pressure pump is linked together with reaction cavity, high-pressure agitator respectively, is provided with micro-nano bubble generator and high-pressure ionization gasification generator in the reaction cavity. The utility model has the advantages of it is following and effect: the new mechanical structure of this scheme utilization has the effect of safety ring protects, effective accuse algae.

Description

Unmanned ecological active water algae control equipment

Technical Field

The utility model relates to an environmental management technical field, in particular to unmanned ecological active water accuse algae equipment.

Background

With the rapid development of social economy, the water body of the reservoir is polluted due to various reasons, so that the nutrient salts in the water body of the reservoir are enriched in a large amount, particularly, organic matter pollution causes the standard exceeding of total nitrogen and total phosphorus, and the eutrophication of the water body is caused, so that the eutrophication water body provides material conditions for the flooding of algae, particularly, in 4-10 months every year, the algae grows extremely vigorously, the serious threat to the drinking water problem is brought, the normal management order of the reservoir is disturbed, and therefore, the algae prevention and control are well made, the water safety is ensured to be the important part of reservoir management work, and the basic effective guarantee for promoting the stable development of society is also provided.

The protection and treatment of water environment need to be started from two aspects of pollution source control and water body treatment. At present, under the background of 'five-water co-treatment' for years and high-intensity 'environmental protection and supervision' by the nation, point source pollution in various parts of China is generally well controlled, a large number of pollution enterprises are shut down, turned to production or upgraded and reformed by technology, the production can be allowed to be carried out only by standard discharge, even some culture facilities are dismantled and forbidden, and the point source pollution control is basically completely successful. However, the diffused pollution from various non-point sources, especially the pollution from various agricultural non-point sources with high proportion, has not been treated by very effective means at home and abroad. Although the influence of non-point source pollution can be reduced to a certain extent by changing planting and breeding modes, strengthening forest belts, wetland construction and other comprehensive treatment measures, the non-point source pollution can be comprehensively controlled almost impossible. This means that the water environment in China mainly faces the influence of the non-point source pollution in the future.

In the prior art, a chemical method is usually adopted for treatment, various chemical substances are required to be added into a water body in the treatment process of the chemical method, so that chemical secondary pollution is caused, the chemical method is not suitable for drinking water sources, and the chemical method usually treats symptoms and causes no root causes, so that the problem of poor persistence is caused.

SUMMERY OF THE UTILITY MODEL

The utility model aims at providing an unmanned ecological active water accuse algae equipment has the effect of safety ring protects, effective accuse algae.

The above technical purpose of the present invention can be achieved by the following technical solutions: the utility model provides an unmanned ecological active water accuse algae equipment, includes the hull, is provided with high-pressure pump, reaction chamber and high-pressure agitator on the hull, and the water inlet of high-pressure pump is connected with the pipe that absorbs water, and the delivery port of high-pressure pump is connected with the shower, and the high-pressure pump is linked together with reaction chamber, high-pressure agitator respectively, is provided with micro-nano bubble generator and high-pressure ionization gasification generator in the reaction chamber.

By adopting the technical scheme, the micro-nano bubble generator generates a large amount of micro-nano bubbles in the muddy water mixed sewage, the turbidity retention time of the sewage in the reaction cavity can be prolonged, air generates equivalent negative ions after high-pressure ionization treatment, the negative ions are filled into the muddy water mixed sewage, and turbid sludge is subjected to oxidation disinfection treatment so as to reduce the harm of harmful substances to water and aquatic organisms, so that the sludge can be subjected to oxygenation and oxidation disinfection pretreatment; in the treatment process, the hull slowly navigates on the surface of water, deep water type lake reservoir often forms the thermocline in summer, the unable convection current of upper and lower water, when the removal and the water absorption of hull sprayed the process and can carry the lower floor water of temperature to the top layer, the convection current of upper and lower water layer has been accelerated, carry nutrient substance to lower floor water, partly is absorbed by the alga and utilizes, another part realizes subsiding, the higher situation of lower floor water oxygen debt has been remedied simultaneously, effective prevention and control of bloom, emergency treatment and ecological environment quick prosthetic effect have. In addition, the water surface turbidity changes in the running process of the ship body, and the photosynthesis of algae can be inhibited to a certain extent. Therefore, the physical treatment is carried out on the premise of not influencing the water quality of the water body, no chemical medicine is used in the treatment process, the method is safe and reliable, the in-situ remediation treatment is realized, the water quality can be obviously improved in a short time, the aim of restraining the secondary occurrence of the cyanobacterial bloom can be achieved, the self-healing capacity of the water body is improved, and the aim of effectively controlling algae is achieved.

The utility model discloses a further set up to: be provided with the detection case on the hull, be provided with a plurality of detecting instrument in the detection case.

By adopting the technical scheme, the detection instrument can monitor the algae content, the water transparency, the heavy metal content, the pH value and the like in the water body in real time, feed back in time and is convenient to operate.

The utility model discloses a further set up to: the detection instrument comprises a field algae analyzer, a transparency detector, a heavy metal detector and a pH meter.

By adopting the technical scheme, the field algae analyzer can measure and identify the content of chlorophyll a and phytoplankton in the water body, the transparency detector detects the transparency of the water quality, the heavy metal detector is used for detecting the content of heavy metal in the water body, and the pH meter is used for detecting the pH value of the water body in real time.

The utility model discloses a further set up to: an ultrasonic generator is also arranged in the reaction chamber.

Through adopting above-mentioned technical scheme, behind supersonic generator acted on homogeneous mixture, can reduce the silt granule on the one hand, on the other hand can improve the duration of silt granule evenly distributed in aqueous for when homogeneous mixture sprays on the surface of water, silt microparticle distribution is more even.

The utility model discloses a further set up to: the shower sets up in the water absorption pipe, forms the chamber that absorbs water between water absorption pipe inner wall and the shower outer wall, and the tip that the hull was kept away from to the water absorption pipe is provided with water connectors, and a plurality of bar through-holes have been seted up to water connectors's lateral wall, and the bar through-hole is linked together with the chamber that absorbs water, and the export of shower is located water connectors.

By adopting the technical scheme, the water connector is inserted into the sludge at the bottom of the river bed, under the driving action of the high-pressure pump, the muddy water mixed sewage at the bottom of the river bed is sucked into the water suction cavity through the strip-shaped through hole, and the sludge in all directions can be sucked into the water suction pipe from the strip-shaped through hole on the corresponding surface; when the gas-liquid mixed liquid is pumped to the bottom of the riverbed, the gas-liquid mixed liquid can be sprayed out from the strip-shaped through holes to the periphery, and the spraying range is wider

The utility model discloses a further set up to: the water connector is internally provided with a stirring blade which is positioned at the water outlet of the spray pipe.

By adopting the technical scheme, the stirring blade can be driven to rotate by virtue of the impact force of the injection in the injection process.

The utility model discloses a further set up to: the water suction pipe is integrally arranged in an inclined way, and the water connection is horizontally arranged relative to the water suction pipe.

Through adopting above-mentioned technical scheme, with the slope setting of the tub that absorbs water, compare in vertical setting, can reduce the resistance to a certain extent.

The utility model discloses a further set up to: the front end of the water joint is provided with a conical guide surface.

Through adopting above-mentioned technical scheme, when the water service connector stretched into to silt, the hull removed the in-process, can play better not hard up effect to silt through the toper spigot surface.

The utility model discloses a further set up to: still including the pier that charges with hull looks adaptation, the pier that charges is provided with automatic electric pile that fills, and the front end of hull is provided with the interface that charges, and the interface that charges is provided with battery compartment and control electronic box with automatic electric pile grafting cooperation back electric connection that fills on the hull, and the control electronic box links to each other with the interface that charges, is provided with the lithium cell module with control electronic box electric connection in the battery compartment.

Through adopting above-mentioned technical scheme, when the equipment on the hull supplies power inadequately, the hull can move to the pier that charges, and the interface that charges is connected the back with automatic charging pile, can carry out the charging process to the lithium battery module, need not to watch in real time, and it is more convenient to use.

The utility model discloses a further set up to: the wharf that charges is provided with the fixing base, is provided with the dead lever on the fixing base, and the coaxial tight pulley that is provided with on the dead lever is provided with on the hull with tight pulley location fit's rubber clutch blocks, be provided with on the rubber clutch blocks with tight pulley direction complex direction inclined plane.

Through adopting above-mentioned technical scheme, when the hull berthed in the pier that charges, the tight pulley can be spacing to the hull along the inclined plane motion of direction to the rubber clutch blocks on for the hull stops in time.

To sum up, the utility model discloses following beneficial effect has:

1. the method adopts a micro-nano bubble generator and a high-pressure ionization gasification generator, can perform oxidation and disinfection pretreatment on muddy water mixed sewage, fills negative ions into the muddy water mixed sewage, performs oxidation and disinfection treatment on turbid sludge to reduce the harm of harmful substances to water and aquatic organisms, does not use any chemical medicine in the treatment process, is safe and reliable, realizes in-situ remediation treatment, can obviously improve the water quality in a short time, and comprises the control of algae biomass and chlorophyll a content in a treated water area, the regulation of the pH value of the water, the content of nutrient substances and the like; the scheme can achieve the aim of inhibiting the secondary occurrence of the cyanobacterial bloom and improve the self-healing capability of the water body;

2. in the treatment process, the ship body slowly sails on the water surface, the convection of an upper water layer and a lower water layer is accelerated, the effects of effectively preventing and controlling the water bloom, performing emergency treatment and quickly restoring the ecological environment are achieved, and in addition, the turbidity of the water surface is changed in the operation process of the ship body, so that the photosynthesis of algae can be inhibited to a certain degree;

3. the stirring blade can be driven to rotate by the impact force of the jet, and a better stirring effect is achieved.

Drawings

Fig. 1 is a schematic diagram of the overall structural relationship of the embodiment.

Fig. 2 is a schematic diagram of the internal structural relationship of the embodiment.

FIG. 3 is a sectional view showing the internal structure of the barrel and the water passage joint according to the embodiment.

FIG. 4 is a graph showing the trend of the pH value of the reservoir with time in the examples.

Fig. 5 is a graph showing the trend of chlorophyll of the water reservoir with time in the example.

FIG. 6 is a graph showing the time-dependent change in transparency of the reservoir in the example.

In the figure: 1. a hull; 11. a charging interface; 12. a battery compartment; 13. controlling an electric box; 14. A lithium battery module; 15. a rubber friction block; 151. a guide slope; 16. a propeller; 2. a charging dock; 21. automatically charging a pile; 22. a fixed seat; 23. fixing the rod; 24. a fixed wheel; 3. A high pressure pump; 4. a high pressure agitator; 41. stirring the mixture in a kettle; 42. a stirring motor; 5. a suction pipe; 51. a water suction cavity; 6. a reaction chamber; 61. a micro-nano bubble generator; 62. a high pressure ionization gasification generator; 63. an ultrasonic generator; 7. a shower pipe; 8. a water connection joint; 81. a tapered guide surface; 82. a strip-shaped through hole; 83. stirring blades; 9. and (6) a detection box.

Detailed Description

The present invention will be further described with reference to the accompanying drawings.

The utility model provides an unmanned ecological living water accuse algae equipment, as shown in fig. 1-3, including hull 1, with the pier 2 that charges of hull 1 looks adaptation, it is provided with automatic electric pile 21 to charge on the pier 2, the front end of hull 1 is provided with the interface 11 that charges, the interface 11 that charges is with automatic electric pile 21 grafting cooperation back electric connection that charges, be provided with battery compartment 12 and control electronic box 13 on the hull 1, control electronic box 13 links to each other with the interface 11 that charges, be provided with in the battery compartment 12 with control electronic box 13 electric connection's lithium cell module 14. Charging dock 2 is provided with the fixing base 22 that is located both sides, all is provided with dead lever 23 on the fixing base 22, and the coaxial tight pulley 24 that is provided with on dead lever 23 is provided with on the hull 1 with the tight pulley 24 location fit's rubber clutch blocks 15, be provided with on the rubber clutch blocks 15 with tight pulley 24 direction complex direction inclined plane 151. When the equipment power supply on the hull 1 is not enough, the hull 1 can move to the charging dock 2, and after the charging interface 11 is connected with the automatic charging pile 21, the charging process can be carried out on the lithium battery module 14, so that the lithium battery module is not required to be watched in real time, and the use is more convenient. When the ship body 1 is moored at the charging wharf 2, the fixed wheels 24 move to the rubber friction blocks 15 along the guide inclined planes 151, so that the ship body 1 can be limited, and the ship body 1 can be stopped in time.

As shown in fig. 2, still be provided with high-pressure pump 3 on the hull 1, reaction chamber 6 and high-pressure agitator 4, high-pressure agitator 4 includes stirred tank 41, set up in stirred tank 41's agitator motor 42, connect in the stirring leaf subassembly of agitator motor 42 output shaft, the water inlet of high-pressure pump 3 is connected with suction pipe 5, suction pipe 5 wholly inclines to set up in hull 1 afterbody, hull 1 afterbody still is provided with propeller 16, high-pressure pump 3 is linked together with reaction chamber 6, high-pressure agitator 4 respectively through the connecting tube, be provided with micro-nano bubble generator 61, high-pressure ionization gasification generator 62 and supersonic generator 63 in the reaction chamber 6.

As shown in fig. 2 and 3, the spray pipe 7 is connected to the water outlet of the high-pressure pump 3, the spray pipe 7 is disposed in the water suction pipe 5, in other embodiments, a mode that the spray pipe 7 and the water suction pipe 5 are separately disposed may be adopted, a water suction cavity 51 is formed between the inner wall of the water suction pipe 5 and the outer wall of the spray pipe 7, the end portion of the water suction pipe 5 far away from the hull 1 is provided with a water connector 8, the water connector 8 is horizontally disposed relative to the water suction pipe 5, the front end of the water connector 8 is provided with a tapered guide surface 81, the side wall of the water connector 8 is provided with a plurality of strip-shaped through holes 82, the strip-shaped through holes 82 are communicated with the water suction cavity 51, the outlet of the spray pipe 7 is located in the water connector 8, the water connector 8 is provided with a stirring blade 83, and the stirring blade 83 is located at the water outlet of the spray pipe 7. The ship body 1 is also provided with a spraying pipeline communicated with the reaction chamber 6, a control valve component is arranged in the spraying pipeline, and the height of a water outlet of the spraying pipeline is higher than that of the water connector 8. In the treatment process, the water through connector 8 is inserted into sludge at the bottom of the river bed, under the driving action of the high-pressure pump 3, the sludge-water mixed sewage at the bottom of the river bed is sucked into the water suction cavity 51 through the strip-shaped through hole 82, and the sludge in all directions can be sucked into the water suction pipe 5 from the strip-shaped through hole 82 on the corresponding surface; when the gas-liquid mixed liquid is pumped to the bottom of the river bed, the gas-liquid mixed liquid can be sprayed out from the strip-shaped through holes 82 to the periphery, the spraying range is wide, and in the spraying process, the stirring blades 83 can be driven to rotate by means of the impact force of spraying, so that a good stirring effect is achieved. The inclined arrangement of the suction pipe 5 can reduce the resistance to some extent compared with the vertical arrangement. When the water connector 8 extends into the sludge, the sludge can be loosened better through the conical guide surface 81 in the moving process of the ship body 1.

As shown in fig. 2, a detection box 9 is arranged on the ship body 1, and a plurality of detection instruments are arranged in the detection box 9, wherein the detection instruments comprise a field algae analyzer, a transparency detector, a heavy metal detector and a pH meter. The detection instrument can monitor the algae content, the water transparency, the heavy metal content, the pH value and the like in the water body in real time and feed back in time, the operation is convenient, the field algae analyzer can measure and identify the chlorophyll a content and phytoplankton in the water body, the transparency detector detects the transparency of the water quality, the heavy metal detector is used for detecting the heavy metal content in the water body, and the pH meter is used for detecting the pH value of the water body in real time.

The algae control method adopting the equipment comprises the following steps:

step one, imbibing: the water suction pipe 5 extends to the bottom of the river bed, and the muddy water mixed dirty liquid at the river bottom is sucked into the reaction chamber 6 from the water suction pipe 5 through the high-pressure pump 3;

step two, oxidation disinfection treatment: opening the micro-nano bubble generator 61 and the high-pressure ionization gasification generator 62, carrying out micro-bubble and high-pressure pretreatment on the muddy water mixed dirty liquid in the step one to prepare a gas-liquid mixed liquid with nano bubbles, and setting the high-pressure ionization generator to be 5-10 ten thousand volts of high-voltage electricity for high-pressure ionization treatment;

step three, spraying liquid: pumping the gas-liquid mixed liquor obtained in the step (2) to the bottom of the river bed through a high-pressure pump (3) and a spray pipe (7), and mixing the gas-liquid mixed liquor with nano bubbles and sludge at the bottom of the river bed to form muddy water mixed liquor;

step four, secondary liquid absorption and stirring: pumping the muddy water mixed liquid and part of the nano bubbles at the bottom of the water area again through the high-pressure pump 3 and the water suction pipe 5, conveying the muddy water mixed liquid and part of the nano bubbles into the high-pressure stirrer 4 for stirring treatment to prepare uniform mixed liquid, taking a proper amount of the uniform mixed liquid to perform data detection in a detector, and respectively detecting the chlorophyll content, the water quality transparency, the heavy metal content and the pH value;

step five, spraying and aerating: and (3) carrying out ultrasonic vibration treatment on the uniformly mixed liquid prepared in the step (4) by an ultrasonic generator (63), then opening a control valve component of a spraying pipeline to spray the uniformly mixed liquid on the water surface, wherein after the ultrasonic generator (63) acts on the uniformly mixed liquid, on one hand, sludge particles can be reduced, on the other hand, the duration time of uniform distribution of the sludge particles in the water can be prolonged, and when the uniformly mixed liquid is sprayed on the water surface, the sludge particles are uniformly distributed.

And operating the steps I to V in a multi-cycle mode.

The basic working principle of the invention is as follows: the method adopts in-situ treatment, takes ecological restoration as a center, does not add any algae control agent and biological fungi, and uses high-efficiency, environment-friendly and advanced purely physical machinery and novel electronic technology.

In the step 2, in the reaction chamber 6, the micro-nano bubble generator 61 generates a large amount of micro-nano bubbles in the muddy water mixed sewage, so that the turbidity retention time of the sewage can be prolonged, air generates a considerable amount of negative ions after high-pressure ionization treatment, the negative ions are filled into the muddy water mixed sewage, and turbid sludge is subjected to oxidation disinfection treatment so as to reduce the harm of harmful substances to water and aquatic organisms, so that the sludge can be subjected to oxygenation and oxidation disinfection pretreatment; in the liquid spraying process in the step 3, the bottom of the riverbed can be stirred, and harmful substances such as methane, sulfide and the like stored in the sludge are released; step 5, after the uniform mixed solution is sprayed on the water surface, the surface tension of the sludge is large, and when the uniform mixture with the sludge is sprayed on the water surface, the uniform mixture is dispersed into tiny particles, so that the contact area of the sludge particles and the water body is increased, and the flocculation effect is achieved; in addition, after the uniform mixed solution is sprayed, aerated and stirred, the dissolved oxygen in water is directly increased, the oxidation of Fe2+ into Fe3+ is facilitated, Fe3+ is combined with phosphate to form insoluble iron phosphate, and the generated ferric hydroxide colloid can adsorb free phosphorus in overlying water under the neutral condition or alkaline condition of Fe3+, so that the main nutrient substances in the water body are reduced. Therefore, the physical treatment is carried out on the premise of not influencing the water quality of the water body, no chemical medicine is used in the treatment process, the method is safe and reliable, the in-situ remediation treatment is realized, the water quality can be obviously improved in a short time, and the method comprises the steps of controlling the algae biomass and the chlorophyll a content in a treated water area, adjusting the pH value of the water body, adjusting the content of nutrient substances and the like; the scheme can achieve the aim of inhibiting the secondary occurrence of the cyanobacterial bloom and improve the self-healing capability of the water body.

Results and analysis:

as shown in fig. 4, the trend graph of the layered pH value of the water in the reservoir changing with time is shown, the pH values of the surface layer water, the middle layer water and the bottom layer water are respectively detected in each time period, the overall change of the pH value of the reservoir is not obvious during the working period, the pH value of the surface layer water is slightly reduced due to the reduction of algae, and the water body is basically in an alkaline state. The pH value change trends of the middle layer and the bottom layer are basically the same in time, and no obvious fluctuation exists.

As shown in fig. 5, the trend graph of chlorophyll change of water in the reservoir with time is shown, the chlorophyll concentration of four fixed points in the reservoir is detected in each time period, the four sample points have the same change trend and are in a descending trend generally, the four sample points suddenly increase about 5 months and 18 days, and the four sample points start to decrease about 26 days. The maximum values of the four chlorophyll are 140.15 μ g/L, 55.43 μ g/L, 56.53 μ g/L and 87.93 μ g/L in day 16 of 4 months. The lowest values appeared on day 17 of 7 months, 10.78. mu.g/L, 11.55. mu.g/L, 15.2. mu.g/L, 14.49. mu.g/L. The algae control effect of the algae control equipment is obvious and has continuity.

The reason for the sudden increase of the chlorophyll concentration in the day of 5 months and 18 days is deduced through the integrated data, namely (1) the flow rate of continuous rainfall upstream is increased from 5 months, 12 days to 16 days, a large amount of nutrient salts are carried, the nitrogen concentration rises suddenly, and the algae migration is accelerated by opening a gate and discharging water; (2) the precipitation damages the growth environment of the algae, the transparency is reduced to the minimum in about 18 days, and the water body is mixed, so that the growth environment of the original algae is changed. (3) After the rainfall is finished, the growth environment of the algae is recovered under the conditions of sufficient sunlight, temperature, total nitrogen and the like 18 days later, the algae grow and propagate rapidly, the chlorophyll a concentration on the surface layer is increased again, and the rainfall has a stage inhibiting effect on the outbreak of the water bloom, but the rainfall does not last for a long time.

As shown in fig. 6, the graph is a trend graph of the change of the transparency of the water in the reservoir with time, the transparency of the water at four points in the reservoir is detected at each time period, and the transparency of the water at the four points is in a descending trend, which shows that the algae control device has an obvious algae control effect and better persistence.

As shown in Table 1, the data table shows the average value and standard deviation of 5 heavy metals in water samples of water bodies at four points of reservoirs S1, S2, S3 and S4, and the average value and standard deviation are compared with the national recommended water quality standard of the U.S. priority pollutants (USEPA 2009) and the environmental quality standard of surface water in China (GB 3838-2002). Through obtaining the parallel contrastive analysis of the dissolved heavy metal level in the water body of four points, the heavy metals Cr and Cd are all relatively low at each point, and the heavy metal Mn all appears at the bottom of each point to the maximum value, but does not exceed the I-grade quality standard of surface water. The content of 5 heavy metals (Cu, Pb, Cr, Cd and Mn) in the reservoir is lower than the class I water quality standard of the surface water environment quality standard, and the phenomenon of heavy metal enrichment does not occur. The water quality of each water body of the reservoir is good, wherein the national recommended water quality standard of the U.S. preferred pollutants (USEPA 2009) aims to protect aquatic organisms, the average amount of heavy metals in each point water body is lower than the continuous reference concentration CCC of the U.S. water quality standard (CCC is the national recommended water quality standard continuous reference concentration USEPA 2009) of the preferred pollutants, and CMC is the maximum reference concentration (USEPA 2009) of the national recommended water quality standard of the preferred pollutants, which indicates that the water bodies at each point are not polluted by the heavy metals and cannot cause chronic toxic consequences.

The comparison of the working period of the algae-controlling ship and the observation period after the work is finished shows that the content of heavy metal in the two periods has little change difference, the three heavy metals of copper, manganese and cadmium have a descending trend, and lead and chromium have a slightly rising phenomenon compared with the working period of the algae-controlling ship. This is probably because 7, 8 months divide and reach the abundant water period of reservoir, and precipitation is more, and upstream pollutant is washed down and is caused, but its content still is less than surface water I class water standard, indicates that the influence is little.

And the comparison of the data of the two periods is integrated, so that the heavy metal pollution to the reservoir can be avoided when the algae control ship works in the reservoir.

TABLE 1 average heavy metal content (μ g/L) in different water layers of reservoir sampling points

The quality standard of surface water is GB 3838-2002; CCC is the national recommended water quality benchmark continuous reference concentration for the priority pollutants (USEPA 2009); CMC is the national recommended water quality benchmark maximum benchmark concentration for the priority pollutants (USEPA 2009).

In conclusion, the algae bloom can be quickly and effectively controlled by the technical treatment of the invention, and the method for controlling the bathing is a bathing control method which has the advantages of quick effect, low cost, no pollution and easy operation.

The above is only the preferred embodiment of the present invention, so all the equivalent changes or modifications made by the structure, features and principles in accordance with the claims of the present invention are included in the claims of the present invention.

Claims (10)

1. An unmanned ecological living water accuse algae equipment which characterized in that: including hull (1), be provided with high-pressure pump (3), reaction chamber (6) and high pressure agitator (4) on hull (1), the water inlet of high-pressure pump (3) is connected with and absorbs water tub (5), the delivery port of high-pressure pump (3) is connected with shower (7), high-pressure pump (3) respectively with reaction chamber (6), high pressure agitator (4) are linked together, be provided with micro-nano bubble generator (61) and high pressure ionization gasification generator (62) in reaction chamber (6).

2. The unmanned ecological activated water algae control apparatus according to claim 1, wherein: the ship body (1) is provided with a detection box (9), and a plurality of detection instruments are arranged in the detection box (9).

3. The unmanned ecological activated water algae control apparatus according to claim 2, wherein: the detection instrument comprises a field algae analyzer, a transparency detector, a heavy metal detector and a pH meter.

4. The unmanned ecological activated water algae control apparatus according to claim 1, wherein: an ultrasonic generator (63) is also arranged in the reaction chamber (6).

5. The unmanned ecological activated water algae control apparatus according to any one of claims 1 to 4, wherein: the spray pipe (7) set up in absorb water in the pipe (5), absorb water pipe (5) inner wall with form between spray pipe (7) outer wall and absorb water chamber (51), it keeps away from to absorb water pipe (5) the tip of hull (1) is provided with leads to water joint (8), a plurality of bar through-holes (82) have been seted up to the lateral wall that leads to water joint (8), bar through-hole (82) with absorb water chamber (51) and be linked together, just the export of spray pipe (7) is located lead to in the water joint (8).

6. The unmanned ecological activated water algae control equipment according to claim 5, wherein: and a stirring blade (83) is arranged in the water connection joint (8), and the stirring blade (83) is positioned at the water outlet of the spray pipe (7).

7. The unmanned ecological activated water algae control equipment according to claim 5, wherein: the water suction pipe (5) is integrally and obliquely arranged, and the water passing joint (8) is horizontally arranged relative to the water suction pipe (5).

8. The unmanned ecological activated water algae control apparatus according to claim 7, wherein: the front end of the water passing joint (8) is provided with a conical guide surface (81).

9. The unmanned ecological activated water algae control apparatus according to claim 1, wherein: still including with charging dock (2) of hull (1) looks adaptation, be provided with automatic electric pile (21) of filling on charging dock (2), the front end of hull (1) is provided with interface (11) that charge, interface (11) that charge with automatic electric pile (21) grafting cooperation back electric connection, be provided with battery compartment (12) and control electronic box (13) on hull (1), control electronic box (13) with interface (11) that charge links to each other, be provided with in battery compartment (12) with control electronic box (13) electric connection's lithium cell module (14).

10. The unmanned ecological activated water algae control apparatus according to claim 9, wherein: charging dock (2) is provided with fixing base (22), be provided with dead lever (23) on fixing base (22), coaxial tight pulley (24) that is provided with on dead lever (23), be provided with on hull (1) with tight pulley (24) location fit's rubber friction block (15), be provided with on rubber friction block (15) with tight pulley (24) direction complex direction inclined plane (151).

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