CN113880235A - Solar energy combined type electrolysis sewage treatment flotation device - Google Patents

Solar energy combined type electrolysis sewage treatment flotation device Download PDF

Info

Publication number
CN113880235A
CN113880235A CN202111355539.5A CN202111355539A CN113880235A CN 113880235 A CN113880235 A CN 113880235A CN 202111355539 A CN202111355539 A CN 202111355539A CN 113880235 A CN113880235 A CN 113880235A
Authority
CN
China
Prior art keywords
floating body
sewage treatment
aeration
solar
biological filler
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.)
Granted
Application number
CN202111355539.5A
Other languages
Chinese (zh)
Other versions
CN113880235B (en
Inventor
郭研
夏建新
宋艳伟
王欢
刘彦
王筱芊
于野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jilin Jianzhu University
Original Assignee
Jilin Jianzhu University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Jilin Jianzhu University filed Critical Jilin Jianzhu University
Priority to CN202111355539.5A priority Critical patent/CN113880235B/en
Publication of CN113880235A publication Critical patent/CN113880235A/en
Application granted granted Critical
Publication of CN113880235B publication Critical patent/CN113880235B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00—Biological treatment of water, waste water, or sewage
    • C02F3/005—Combined electrochemical biological processes
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104—Devices therefor; Their operating or servicing
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00—Biological treatment of water, waste water, or sewage
    • C02F3/02—Aerobic processes
    • C02F3/12—Activated sludge processes
    • C02F3/1236—Particular type of activated sludge installations
    • C02F3/1268—Membrane bioreactor systems
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00—Biological treatment of water, waste water, or sewage
    • C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24—HEATING; RANGES; VENTILATING
    • F24S—SOLAR HEAT COLLECTORS; SOLAR HEAT SYSTEMS
    • F24S25/00—Arrangement of stationary mountings or supports for solar heat collector modules
    • H—ELECTRICITY
    • H02—GENERATION; CONVERSION OR DISTRIBUTION OF ELECTRIC POWER
    • H02S—GENERATION OF ELECTRIC POWER BY CONVERSION OF INFRARED RADIATION, VISIBLE LIGHT OR ULTRAVIOLET LIGHT, e.g. USING PHOTOVOLTAIC [PV] MODULES
    • H02S20/00—Supporting structures for PV modules
    • 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
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00—Water conservation; Efficient water supply; Efficient water use
    • Y02A20/20—Controlling water pollution; Waste water treatment
    • Y02A20/208—Off-grid powered water treatment
    • Y02A20/212—Solar-powered wastewater sewage treatment, e.g. spray evaporation
    • 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
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E10/00—Energy generation through renewable energy sources
    • Y02E10/40—Solar thermal energy, e.g. solar towers
    • Y02E10/47—Mountings or tracking
    • 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
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E10/00—Energy generation through renewable energy sources
    • Y02E10/50—Photovoltaic [PV] energy
    • 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
    • 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

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Microbiology (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • General Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • Combustion & Propulsion (AREA)
  • Sustainable Development (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Sustainable Energy (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention relates to the technical field of sewage treatment in environmental engineering discipline, in particular to a solar combined type electrolysis sewage treatment floating device. The invention constructs two sewage treatment modes in space, skillfully designs an oxygen conveying mode by a biofilm method, integrates and supports the biological filler main rod and the aeration branch pipe, increases the sewage treatment depth by the telescopic electrode, enlarges the sewage treatment space, overcomes the electrolytic function obstruction caused by the winding and the attachment of impurities such as flocculent precipitates and the like on the electrode in the electrolytic method, improves the electrode efficiency and has good effect.

Description

Solar energy combined type electrolysis sewage treatment flotation device
Technical Field
The invention relates to the technical field of sewage treatment in environmental engineering discipline, in particular to a solar combined type electrolysis sewage treatment floating device.
Background
The electrolytic process for treating sewage is a process of purifying sewage by utilizing oxidation-reduction reaction of a cathode and an anode, taking the sewage as an electrolyte solution and through electrochemical action, indirect oxidation or reduction action, particle polarization, electro-flotation action, electro-flocculation action and the like. When the anode is made of soluble Fe and Al, porous flocculent (or gelatinous) metal hydroxide is formed, and can perform coagulation on suspended matters, particles, organic or inorganic pollutants in the sewage through surface adsorption, charge action and the like, so that the water quality is purified.
The electrolysis sewage treatment method has the advantages that: the direct current power supply supplies power, so that a large amount of chemical agents are not required to be input, and secondary pollution to a water body is avoided; the voltage can be adjusted to deal with the change of the concentration of the pollutants in the water; the effluent quality is stable, the device is simple and easy to operate, and the occupied area is small.
The biomembrane process water treatment technology is a process of utilizing certain solid carriers to construct living space of microorganisms and carrying out treatment on organic sewage under the action of nutrients. The larger the specific surface area of the biological filler is, the easier more microorganisms are attached, and the better the water treatment effect is.
According to the prior art, the defects of the electrolytic method for treating the sewage are as follows: power consumption, a sufficient supply of electricity is required; when the anode material is a soluble material (i.e. the electrode material loses electrons and enters the chemical reaction of the solution in the form of ions), flocculent precipitates and impurities formed after a long time are easy to attach to the anode region, and the operation of an electrode bar (an electrode plate) is hindered.
If the water body is seriously polluted, the dissolved amount of oxygen is low, which is very unfavorable for the microbial decomposition on the biological filler. Moreover, the traditional biological filler, such as a suspended biological filler, is easy to cause the phenomena of agglomeration, broken filaments, mutual winding and the like after long-term use.
In order to solve the problems, the solar combined type electrolysis sewage treatment floating device can effectively avoid the defects, achieve reasonable design and breakthrough the traditional water treatment scheme.
Disclosure of Invention
Technical problem to be solved
The invention aims at the technical problems provided by the background technology and provides a solar combined type electrolysis sewage treatment floating device.
(II) technical scheme
A solar energy combined type electrolysis sewage treatment floating device comprises a hollow floating body, a floating device and a control device, wherein the hollow floating body is used for installing all system components and can float in water;
the solar power generation control system is arranged at the top of the hollow floating body and used for supplying power to the electrochemical treatment system;
the electrochemical treatment system is arranged in the lower part of the hollow floating body and is used for treating sewage by an electrolytic method;
the biomembrane method treatment system is arranged on the outer ring of the hollow floating body and is used for treating sewage by a biomembrane method.
Preferably, the solar power generation control system comprises a hollow floating body, a solar panel, a controller and an electric wire;
the solar cell panel is arranged in the central area of the flat cylindrical hollow floating body, the controller and part of electric wires are positioned in the cavity of the hollow floating body, and other electric wires are linked in the circuit.
Preferably, the electrochemical treatment system comprises a telescopic rod, a cathode rod and an anode rod,
the two telescopic rods are arranged at intervals, and are used for fixing the bottom end of the hollow floating body and are positioned at the inner side of the annular aeration main pipe; the cathode bar and the anode bar are respectively fixed on the telescopic rods and are supplied with direct current power by the solar cell panel; the controller intelligent controller is provided with a telescopic rod with a positive electrode and a negative electrode, so that the telescopic rod can stretch and rotate in multiple stages.
Preferably, the biofilm method treatment system comprises a biological filler main rod, a biological filler beard rope, a fan and an aeration pipeline;
the aeration pipeline is divided into an aeration main pipe and aeration branch pipes, the aeration main pipe is fixed at the bottom end of the hollow floating body and is annular, a plurality of round holes are arranged on the aeration main pipe, and the round holes are hermetically connected with the arc-shaped aeration branch pipes;
the biological filler main rod is fixed among the plurality of aeration branch pipes, and the biological filler main rod and the aeration branch pipes play a mutual supporting role but are not communicated in the pipes; the biological filler beard rope is a plurality of fine filaments on the main biological filler rod, and the specific surface area of the biological filler is increased;
the fan is positioned at the central point on the hollow floating body to keep the balance of the floating body; the air outlet of the fan penetrates through the hollow floating body and is connected with the main aeration pipe at the bottom end of the floating body.
Preferably, the voltage provided by the solar power system is set according to the electrolysis requirements.
Preferably, the silica gel ring is embedded around the hollow floating body, and the fixing ring is arranged outside the hollow floating body.
Preferably, the cathode bar and the anode bar are detachably mounted and connected with the telescopic rod and can be replaced at any time.
Preferably, the biological filler main rod is made of polypropylene or polyethylene or modified materials thereof; the biological filler must be fixed on the biological filler main rod by a rope.
Preferably, the outlet of the aeration branch pipe is provided with a grid to prevent floating objects from entering the pipeline; the aeration branch pipes and the biological filler main rod form an arc-shaped outer cover and a grid structure which are mutually supported at the periphery of the device.
Preferably, the device is equipped with a microbial cartridge; the microbial tube is an accessory, the upper end of the tube body is spirally fixed at the bottom end of the floating body and can be detached at any time;
the microbial tube is a small microbial culture dish, the bottom end of the microbial tube is provided with a microbial liquid dispersion hole and an outer sealing cover; the microbial tube is used for modulating and domesticating microbes and can be configured according to the requirement of the microbial content in water.
(III) advantageous effects
The invention provides a solar combined type electrolytic sewage treatment floating device, which has the following advantages:
1. the application range of the electrolysis method for treating sewage is expanded, the floating type water treatment device works in a water body and is movable, and the water area treatment area is increased.
2. The combined action of the electrolysis method and the biomembrane method is utilized, so that the mode of independently treating the sewage by the electrolysis method and the biomembrane method is changed. The two supplement each other, enhancing the water treatment effect.
3. The device is powered by a solar power generation system, and the controller automatically operates to ensure power supply.
4. The cathode and anode are driven by a plurality of sections of telescopic rods, and meanwhile, the telescopic rods can rotate to carry out electrolysis work on water bodies at different depths, so that the treatment space is increased; the telescopic link mode can be decided by oneself, and the flexible and rotation of telescopic link has effectively overcome the electrolytic function that debris such as flocculent precipitate caused because of the winding (attached) to the electrode and has hindered in the electrolytic method, has improved electrode efficiency, and the effect is good.
5. The biological filler on the arc-shaped outer cover of the device has rich biological filler beard ropes with large specific surface area, the beard ropes are attached to the filler main pipe, the structure is stable and firm, and the design avoids the phenomena of easy conglomeration, easy yarn breakage, easy winding, easy blockage and the like of the traditional filler when used for a long time.
6. The aeration branch pipes and the biological filler main pipe form a lantern-shaped grid structure which are independent from each other and are mutually supported at the periphery of the device.
7. The oxygen delivery mode is skillfully designed, and oxygen is supplied from the fan, the main aeration pipe and the branch aeration pipe from top to bottom at any time, so that a good oxygen-enriched environment is provided for microorganisms.
8. For the microorganism content of abundant water, the device has been equipped with the microbial srain, is a small-size microorganism culture dish, is used for carrying the fungus liquid after intaking, promotes water treatment effect.
9. Overcomes the problem of electrolytic function obstruction caused by the winding (attachment) of impurities such as flocculent precipitate on the electrode in the electrolytic method, improves the electrode efficiency and has good effect.
10. The silica gel ring is embedded around the hollow floating body, so that the device is prevented from colliding with other objects, and a buffering effect is achieved.
11. The device has the advantages of simple manufacturing process, attractive design, easy operation, energy conservation and emission reduction.
Drawings
In order to more clearly illustrate the technical solutions of the embodiments of the present invention, the drawings used in the description of the embodiments will be briefly introduced below, and it is obvious that the drawings in the following description are only for the present invention and protect some embodiments, and it is obvious for those skilled in the art that other drawings can be obtained according to these drawings without creative efforts.
FIG. 1 is a schematic view of an electrode of a solar combined electrolysis sewage treatment floatation device;
FIG. 2 is a schematic view of a solar hybrid electrolysis wastewater treatment floatation device (without biological filler beard rope);
FIG. 3 is a drawing of the position of the bio-filler beard rope;
fig. 4 is a schematic view of the lower structure of the hollow floating body.
In the drawings, the components represented by the respective reference numerals are listed below:
1-a hollow floating body; 2-aeration main pipe; 3-a solar panel; 4-a fan; 5, a telescopic rod; 6-cathode bar; 7-an anode rod; 8-a microbial tube; 9-microbial liquid dispersion wells; 10-aeration pipe distribution; 11-biological filler main rod; 12-biological filler beard rope; 13-silica gel ring; 14-fixing ring.
Detailed Description
The technical solutions of the present invention will be described clearly and completely with reference to the accompanying drawings, and it should be understood that the described embodiments are some, but not all embodiments of the present invention. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
In the description of the present invention, it should be noted that, as the terms "center", "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc. appear, their indicated orientations or positional relationships are based on those shown in the drawings, and are only for convenience of description and simplicity of description, but do not indicate or imply that the referred device or element must have a specific orientation, be constructed in a specific orientation, and be operated, and thus, should not be construed as limiting the present invention. Moreover, the terms "first," "second," and "third," if any, are used for descriptive purposes only and are not to be construed as indicating or implying relative importance.
In the description of the present invention, it is to be noted that, unless otherwise explicitly specified or limited, the terms "mounted," "connected," and "connected" should be interpreted broadly, e.g., as meaning either a fixed connection, a removable connection, or an integral connection; can be mechanically or electrically connected; they may be connected directly or indirectly through intervening media, or they may be interconnected between two elements. The specific meanings of the above terms in the present invention can be understood in specific cases to those skilled in the art.
Referring to the attached drawings 1-4, a solar combined type electrolysis sewage treatment floating device comprises a hollow floating body 1, a floating device and a control device, wherein the hollow floating body is used for installing various system components and can float in water;
the solar power generation control system is arranged at the top of the hollow floating body 1 and used for supplying power to the electrochemical treatment system;
the electrochemical treatment system is arranged in the lower part of the hollow floating body 1 and is used for treating sewage by an electrolytic method;
the biomembrane method treatment system is arranged on the outer ring of the hollow floating body 1 and is used for treating sewage by a biomembrane method.
The solar power generation control system comprises a hollow floating body 1, a solar panel 3, a controller and an electric wire;
the solar cell panel 3 is arranged in the central area of the flat cylindrical hollow floating body 1, the controller and part of electric wires are positioned in the cavity of the hollow floating body 1, and the rest electric wires are linked in a circuit.
The electrochemical treatment system comprises a telescopic rod 5, a cathode bar 6 and an anode bar 7,
two telescopic rods 5 are arranged at intervals, and the bottom ends of the hollow floating bodies 1 are fixed and positioned at the inner side of the annular aeration main pipe 2; the cathode bar 6 and the anode bar 7 are respectively fixed on the telescopic rod 5, and the cathode bar 6 and the anode bar 7 are supplied with direct current power by the solar cell panel 3; the controller intelligent controller is provided with a telescopic rod 5 with a positive electrode and a negative electrode, so that the telescopic rod 5 can be stretched and rotated in multiple stages;
specifically, the telescopic rod 5 is provided with a multi-stage telescopic mode, so that the depth of electrode treatment water can be increased; the telescopic rod 5 and the hollow floating body are fixed in a spiral thread mode in a rotating mode, the telescopic rod is controlled and operated by the controller, and the setting mode can be self-determined. For example, the device is arranged to be extended for one section, and after the sewage is treated for a period of time, the device is rotated for a few seconds and then retracted to the original position, so that flocculent sediments and partial dirt are removed, and the device has a self-cleaning mode; then the two sections are extended out again, the water treatment is continued, and the operation is repeated in the mode.
Wherein, the anode rod 7 can be selectively provided with an iron rod, an aluminum rod or other improved metals according to the water quality; the cathode rods 6 are made of an inert material such as carbon rods.
The biofilm method treatment system comprises a biological filler main rod 11, a biological filler beard rope 12, a microbial tube 8, a fan 4 and an aeration pipeline;
the aeration pipeline is divided into an aeration main pipe 2 and aeration branch pipes 10, the aeration main pipe 2 is fixed at the bottom end of the hollow floating body 1 and is annular, a plurality of round holes are arranged on the aeration main pipe 2, and the round holes are hermetically connected with the arc-shaped aeration branch pipes 10;
wherein, the biological filler main rod 11 is fixed among a plurality of aeration branch pipes 10, and the biological filler main rod and the aeration branch pipes play a mutual supporting role but are not communicated in the pipes; the biological filler beard rope 12 is a plurality of fine filaments on the biological filler main rod 11, and the specific surface area of the biological filler is increased;
the microbial tube 8 is an accessory, the upper end of the tube body is spirally fixed at the bottom end of the floating body and can be detached at any time;
the fan 4 is positioned at the central point on the hollow floating body 1 to keep the balance of the floating body; the air outlet of the fan 4 passes through the hollow floating body 1 and is connected with the main aeration pipe 2 at the bottom end of the floating body.
The voltage provided by the solar power generation system is set according to the electrolysis requirement, so that the energy is saved and the environment is protected;
a silica gel ring 13 is embedded around the hollow floating body 1 to prevent the device from colliding with other objects and play a role in buffering; the outside of the hollow floating body 1 is provided with a fixed ring 14 for fixing the device;
the cathode bar 6 and the anode bar 7 are detachably mounted and connected with the telescopic rod 5 and can be replaced at any time.
The main biological filler rod 11 is made of polypropylene or polyethylene or modified materials thereof, and the main biological filler rod of the materials is slightly elastic, has certain toughness and certain hardness, and can play a good supporting role; the biological filler beard rope 12 is fixed on the biological filler main rod 11, the structure is simple, and the phenomena of easy conglomeration, easy wire breakage, easy winding, easy blockage and the like in long-time use are effectively avoided
The outlet of the aeration branch pipe 10 is provided with a grid to prevent floating objects from entering the pipeline; the aeration branch pipe 10 and the biological filler main rod 11 form an arc-shaped outer cover and a grid structure which are mutually supported at the periphery of the device.
The microbial tube 8 is a small microbial culture dish, the bottom end of which is provided with a microbial liquid dispersion hole 9 and is provided with an outer sealing cover; the microbial tube 8 is used for modulating and domesticating microbes and can be configured according to the requirement of the microbial content in water.
The operation of the device is described below:
the device is installed and placed: soluble electrode iron (or aluminum and the like) is taken as an anode rod 7 and is arranged in the telescopic rod 5 at the anode end, and an inert electrode is taken as a cathode rod 6 and is arranged in the telescopic rod 5 at the cathode end; adjusting the time and the starting sequence of the controller; the device is placed in the body of water by tying a length of rope to the float retaining ring 14 and securing it in a predetermined position.
The device carries out sewage treatment work: the controller starts a starting mode, the solar power generation pool plate 3 starts to work, and power is generated outwards; the solar panel 3 communicates a direct current power supply to the cathode bar 6 and the anode bar 7.
According to the sequence of a starter of a controller, a section of the telescopic rod 5 is extended out, when a certain voltage is reached, the iron simple substance of the anode rod 7 enters the solution in the form of ferrous ions, and then flocculent Fe (OH) is formed2The precipitate or the jelly has good adsorption performance, has physicochemical action on suspended matters, impurity particles, certain ions and the like in the sewage, or performs potential neutralization on particles with opposite charges;
at the cathode 6, hydrogen ions in the water can obtain electrons to generate hydrogen, and the hydrogen is used as a reducing agent and can reduce nitrate nitrogen under the action of denitrifying bacteria; some other ions contained in the sewage have a competitive relationship of electron gain and loss (namely, a sequential precipitation sequence) in a cathode region and an anode region, oxidation and reduction reactions respectively occur in the anode and the cathode, and harmful substances are removed.
When the electrolysis starts, the controller starts the air 4 to work, and the fan injects air into water through the main aeration pipe 2 and the branch aeration pipe 10, so as to achieve the purpose of oxygen enrichment. And the microorganisms on the biological filler (including the biological filler beard rope 12) begin to process the sewage;
in the process, according to the preset time and working mode, the controller rotates the telescopic rod 5 for a few seconds at a certain rotating speed and retracts the telescopic rod to the original position, so that flocculent precipitates and partial dirt are thrown away, and the self-cleaning mode is realized; then the controller sends out an instruction again to stretch out two sections again, sewage treatment is continued, and the operation is repeated in the mode.
If additional microorganisms are required, the microorganism tube 8 may be provided and the microorganism tube 8 may be pre-installed on the device.
The device is suitable for large open water bodies and small semi-closed water bodies; in one embodiment, the device has a transverse diameter of 2000mm and a wading depth of 2000 mm; of course, the device can be enlarged in size as required.
In addition, the solar power generation system of the device can be supplied with power by a storage battery instead.
It should be noted that the control method of the electrical components is the prior art, and is explained here in order to avoid redundancy of description; and the present application is primarily intended to protect mechanical equipment, the control means and circuit connections will not be explained in detail herein.
In the description herein, references to the description of "one embodiment," "an example," "a specific example" or the like are intended to mean that a particular feature, structure, material, or characteristic described in connection with the embodiment or example is included in at least one embodiment or example of the invention. In this specification, the schematic representations of the terms used above do not necessarily refer to the same embodiment or example. Furthermore, the particular features, structures, materials, or characteristics described may be combined in any suitable manner in any one or more embodiments or examples.
The preferred embodiments of the invention disclosed above are intended to be illustrative only. The preferred embodiments are not intended to be exhaustive or to limit the invention to the precise forms disclosed. Obviously, many modifications and variations are possible in light of the above teaching. The embodiments were chosen and described in order to best explain the principles of the invention and the practical application, to thereby enable others skilled in the art to best utilize the invention. The invention is limited only by the claims and their full scope and equivalents.

Claims (10)

1. A solar energy combined type electrolysis sewage treatment floating device is characterized by comprising a hollow floating body (1) which is used for installing each system component and can float in water;
the solar power generation control system is arranged at the top of the hollow floating body (1) and is used for supplying power to the electrochemical treatment system;
the electrochemical treatment system is arranged in the lower part of the hollow floating body (1) and is used for treating sewage by an electrolytic method;
the biomembrane method treatment system is arranged on the outer ring of the hollow floating body (1) and treats sewage by a biomembrane method.
2. The solar combined type sewage treatment floating device adopting electrolysis method according to claim 1, wherein the solar power generation control system comprises a hollow floating body (1), a solar cell panel (3), a controller and an electric wire;
the solar cell panel (3) is arranged in the central area of the flat cylindrical hollow floating body (1), the controller and part of electric wires are positioned in the cavity of the hollow floating body (1), and the rest of electric wires are linked in a circuit.
3. The solar energy composite electrolysis sewage treatment floating device according to claim 2, wherein the electrochemical treatment system comprises a telescopic rod (5), a cathode rod (6) and an anode rod (7),
the two telescopic rods (5) are arranged at intervals, and are used for fixing the bottom end of the hollow floating body (1) and are positioned at the inner side of the annular aeration main pipe (2); the cathode bar (6) and the anode bar (7) are respectively fixed on the telescopic rod (5), and the cathode bar (6) and the anode bar (7) are supplied with a direct current power supply by the solar cell panel (3); the controller intelligent controller is provided with a telescopic rod (5) with a positive electrode and a negative electrode, so that the telescopic rod (5) can be stretched and rotated in multiple stages.
4. The solar combined type electrolytic wastewater treatment floating device according to claim 3, wherein the biofilm method treatment system comprises a biofilm filler main rod (11), a biofilm filler beard rope (12), a fan (4) and an aeration pipeline;
the aeration pipeline is divided into an aeration main pipe (2) and aeration branch pipes (10), the aeration main pipe (2) is fixed at the bottom end of the hollow floating body (1) and is annular, a plurality of round holes are arranged on the aeration main pipe (2), and the round holes are hermetically connected with the arc-shaped aeration branch pipes (10);
the biological filler main rod (11) is fixed among the aeration branch pipes (10), and the biological filler main rod and the aeration branch pipes play a mutual supporting role but are not communicated in the pipes; the biological filler beard rope (12) is a plurality of fine filaments on the biological filler main rod (11), and the specific surface area of the biological filler is increased;
the fan (4) is positioned at the central point on the hollow floating body (1) to keep the balance of the floating body; the air outlet of the fan (4) penetrates through the hollow floating body (1) and is connected with the aeration main pipe (2) at the bottom end of the floating body.
5. The solar energy combined electrolysis sewage treatment floating device according to claim 4, wherein the voltage provided by the solar power generation system is set according to the electrolysis requirement.
6. The solar combined type floating device for sewage treatment by electrolysis according to claim 5, wherein a silica gel ring (13) is embedded around the hollow floating body (1), and a fixing ring (14) is arranged outside the hollow floating body (1).
7. The solar energy combined type electrolysis sewage treatment floating device according to claim 5, wherein the cathode bar (6) and the anode bar (7) are detachably connected with the telescopic bar (5) and can be replaced at any time.
8. The solar combined type electrolytic process sewage treatment floating device according to claim 5, wherein the biological filler main rods (11) are made of polypropylene or polyethylene, or modified materials thereof; the biological filler beard rope (12) is fixed on the biological filler main rod (11).
9. The solar combined electrolysis sewage treatment floating device according to claim 5, wherein the outlet of the aeration branch pipe (10) is provided with a grid to prevent floating objects from entering the pipeline; the aeration branch pipe (10) and the biological filler main rod (11) form an arc-shaped outer cover and a grid structure which are mutually supported at the periphery of the device.
10. The solar combined type electrolysis sewage treatment floating device according to claim 5, further comprising a microbial tube (8); the microbial tube (8) is an accessory, the upper end of the tube body is spirally fixed at the bottom end of the floating body and can be detached at any time;
the microbial tube (8) is a small microbial culture dish, the bottom end of the microbial tube is provided with a microbial liquid dispersion hole (9) and an outer sealing cover; the microorganism tube (8) is used for modulating and domesticating microorganisms and can be configured according to the requirement of the microorganism content in water.
CN202111355539.5A 2021-11-16 2021-11-16 Solar energy combined type electrolysis sewage treatment flotation device Active CN113880235B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111355539.5A CN113880235B (en) 2021-11-16 2021-11-16 Solar energy combined type electrolysis sewage treatment flotation device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111355539.5A CN113880235B (en) 2021-11-16 2021-11-16 Solar energy combined type electrolysis sewage treatment flotation device

Publications (2)

Publication Number Publication Date
CN113880235A true CN113880235A (en) 2022-01-04
CN113880235B CN113880235B (en) 2023-03-07

Family

ID=79017681

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111355539.5A Active CN113880235B (en) 2021-11-16 2021-11-16 Solar energy combined type electrolysis sewage treatment flotation device

Country Status (1)

Country Link
CN (1) CN113880235B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116495824A (en) * 2023-05-05 2023-07-28 浙江省生态环境科学设计研究院 Solar floating type water algae inhibition equipment

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005279482A (en) * 2004-03-30 2005-10-13 Hitachi Kiden Kogyo Ltd Electrolytic treatment device
JP2006110482A (en) * 2004-10-15 2006-04-27 Mitsubishi Heavy Ind Ltd Method and system for treating liquid organic waste
CN101367579A (en) * 2008-09-27 2009-02-18 东华大学 High-efficiency hollow grid shaped spherical suspending filling material
CN105923956A (en) * 2016-07-04 2016-09-07 河海大学 Movable solar electroosmotic soft soil reinforcement device system and application method thereof
CN107459127A (en) * 2017-07-13 2017-12-12 盐城工学院 A kind of regulation and control municipal wastewater pipeline sulphur conversion system in situ and its operation method
CN208394949U (en) * 2018-01-24 2019-01-18 广东欧沃环境科技有限公司 A kind of novel purification tank for liquid waste
CN210340638U (en) * 2019-08-16 2020-04-17 蚌埠学院 Electrocatalytic oxidation device for sewage treatment
CN211595191U (en) * 2019-12-19 2020-09-29 南京信息工程大学 Combined type chinampa wetland purifier

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005279482A (en) * 2004-03-30 2005-10-13 Hitachi Kiden Kogyo Ltd Electrolytic treatment device
JP2006110482A (en) * 2004-10-15 2006-04-27 Mitsubishi Heavy Ind Ltd Method and system for treating liquid organic waste
CN101367579A (en) * 2008-09-27 2009-02-18 东华大学 High-efficiency hollow grid shaped spherical suspending filling material
CN105923956A (en) * 2016-07-04 2016-09-07 河海大学 Movable solar electroosmotic soft soil reinforcement device system and application method thereof
CN107459127A (en) * 2017-07-13 2017-12-12 盐城工学院 A kind of regulation and control municipal wastewater pipeline sulphur conversion system in situ and its operation method
CN208394949U (en) * 2018-01-24 2019-01-18 广东欧沃环境科技有限公司 A kind of novel purification tank for liquid waste
CN210340638U (en) * 2019-08-16 2020-04-17 蚌埠学院 Electrocatalytic oxidation device for sewage treatment
CN211595191U (en) * 2019-12-19 2020-09-29 南京信息工程大学 Combined type chinampa wetland purifier

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116495824A (en) * 2023-05-05 2023-07-28 浙江省生态环境科学设计研究院 Solar floating type water algae inhibition equipment
CN116495824B (en) * 2023-05-05 2023-12-29 浙江省生态环境科学设计研究院 Solar floating type water algae inhibition equipment

Also Published As

Publication number Publication date
CN113880235B (en) 2023-03-07

Similar Documents

Publication Publication Date Title
CN102381753B (en) Bioelectrochemical film reactor device
US20100304226A1 (en) Microbial fuel cell
KR101163365B1 (en) Floating-type microbial fuel cell
CN101857309A (en) Electrochemical biological combined denitrification reactor
CN104628090A (en) Bio-electrochemical reactor and application thereof in degrading fluoronitrobenzene wastewater
CN112573667A (en) Sewage treatment device and method based on phycomycete symbiotic electrochemical system
CN108178289A (en) A kind of enhanced aeration ecological restoration device
CN113880235B (en) Solar energy combined type electrolysis sewage treatment flotation device
CN107010728B (en) Gradual change type completely autotrophic nitrogen removal system and treatment method thereof
CN111925044B (en) Sequencing batch biofilm-electrolysis treatment and recycling device and method for domestic sewage
CN1600699A (en) Equipment and method for treating organic waste water through electrocatalysis of cathode in combination with anode
CN111584913B (en) Vertical current reciprocal type microbial fuel cell
CN112897818A (en) Purification system and method capable of controlling release of endogenous phosphorus in water body
CN110156148A (en) It is a kind of to strengthen pollution cutting device for the electrolysis for entering river pollution
KR101040185B1 (en) Microbial fuel cell unit equipped with functional electrodes and microbial fuel cell prepared therewith
CN218709624U (en) Bioelectricity reinforced combination device for treating antibiotic-containing biogas slurry
CN202912755U (en) Device for treating organic wastewater via electric field ozone compound catalysis and oxidation
CN107010729B (en) Gas-water anisotropic flow gradual-change type completely autotrophic nitrogen removal system and treatment method thereof
CN201722209U (en) Electrochemical biological combined denitrification reactor
CN209721886U (en) A kind of electricity production 20-87W/m2Energy conservation catalysis water treatment facilities
CN113429075A (en) Black-odor river restoration system and application thereof
CN217808937U (en) Electric auxiliary vertical flow constructed wetland reactor
CN215102544U (en) electro-Fenton effluent treatment plant
CN106007175B (en) A kind of persistence organic pollutant removal system based on artificial swamp
CN102324543B (en) Microbial fuel cell with naturally oxygenated biological cathode

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant