CN210936404U - Novel intelligent organic garbage treatment system - Google Patents
Novel intelligent organic garbage treatment system Download PDFInfo
- Publication number
- CN210936404U CN210936404U CN201921546166.8U CN201921546166U CN210936404U CN 210936404 U CN210936404 U CN 210936404U CN 201921546166 U CN201921546166 U CN 201921546166U CN 210936404 U CN210936404 U CN 210936404U
- Authority
- CN
- China
- Prior art keywords
- tank
- liquid
- anaerobic fermentation
- organic garbage
- receiving
- 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.)
- Active
Links
Images
Classifications
-
- 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
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- 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
- Y02W30/00—Technologies for solid waste management
- Y02W30/20—Waste processing or separation
Abstract
The utility model discloses a novel intelligent organic garbage treatment system, which comprises a crushing device, wherein the crushing device is used for crushing organic garbage; the adjusting tank is used for receiving the organic garbage in the crushing device, strains mixed with the organic garbage are added in the adjusting tank, and a heating system and a first stirring system are arranged in the adjusting tank; the anaerobic fermentation bin is used for receiving a mixture of the organic garbage and the strains in the regulating reservoir, a first temperature control device and a second stirring system are arranged in the anaerobic fermentation bin, and the second stirring system is used for stirring the mixture of the organic garbage and the strains to generate methane, biogas slurry and biogas residues; the gas box is used for storing methane generated by the anaerobic fermentation chamber; the water collecting tank is used for receiving the liquid fermented by the anaerobic fermentation chamber; the three-phase separation reactor is used for receiving liquid with the temperature adjusted in the collecting pool, and the three-phase separation reactor separates the liquid into slag, methane and separation liquid. The utility model discloses can adopt biodegradable organic refuse treatment technique, power loss is less, and the treatment effect is good.
Description
Technical Field
The utility model belongs to the refuse treatment field, more specifically the novel intelligent organic refuse treatment system that says so.
Background
With the continuous and high-speed development of economic society, garbage disposal becomes an important subject influencing environmental protection, resident life and sustainable development, and if the domestic garbage can not be scientifically and effectively treated, the garbage disposal not only pollutes the environment and destroys the ecology, but also spreads diseases, threatens the harmonious coexistence of people and nature, and influences the daily life of people.
In recent years, garbage disposal has been paid attention from various aspects, and based on the original simple treatment such as landfill, incineration and compost, garbage classification and resource utilization are comprehensively carried out; at present, methods such as sunlight room compost fermentation treatment, machine biological fermentation rapid fertilization treatment, gasification pyrolysis furnace treatment, biological cultivation degradation treatment, common biogas anaerobic fermentation treatment and the like are mainly adopted, but any treatment mode has respective limitations: 1. the degradation effect of the compost fermentation treatment in the sunlight room is poor, and mosquitoes and flies are easy to breed and diseases are easy to spread; 2. the cost of the quick fertilizer-forming treatment of the mechanical biological fermentation and the operation and maintenance of the gasification pyrolysis furnace treatment is high, the subsequent garbage can not be effectively treated in time after the equipment failure, and the building index which is quite short originally is occupied; 3. the land area occupied by the biological culture degradation treatment is large, and the requirement of rapid garbage growth cannot be met by daily treatment; 4. the land area occupied by the common anaerobic fermentation treatment of the methane is large, and the method is not suitable for large-scale and municipal waste treatment.
SUMMERY OF THE UTILITY MODEL
Not enough to prior art, the utility model provides a high efficiency energy-conservation practices thrift the novel intelligent organic refuse treatment system in soil.
In order to achieve the above purpose, the utility model provides a following technical scheme: novel intelligent organic garbage disposal system, include
The crushing device is used for crushing the organic garbage;
the adjusting tank is used for receiving the organic garbage in the crushing device, strains mixed with the organic garbage are added in the adjusting tank, and a heating system and a first stirring system are arranged in the adjusting tank;
the anaerobic fermentation bin is used for receiving a mixture of the organic garbage and the strains in the regulating reservoir, a first temperature control device and a second stirring system are arranged in the anaerobic fermentation bin, the temperature control device is used for controlling the temperature in the anaerobic bin, and the second stirring system is used for stirring the mixture of the organic garbage and the strains to generate methane, biogas slurry and biogas residues;
the gas tank is used for storing methane generated by the anaerobic fermentation bin;
the water collecting tank is used for receiving the liquid fermented by the anaerobic fermentation bin, and a second temperature control device is arranged in the water collecting tank and used for adjusting the temperature of the liquid in the water collecting tank;
the three-phase separation reactor is used for receiving and collecting liquid with the temperature adjusted in the water tank, the three-phase separator separates the liquid into slag, methane and separation liquid, the slag is discharged to the anaerobic fermentation chamber, and the methane is discharged to the gas tank;
the middle adjusting tank is used for receiving the separation liquid separated by the three-phase separator, a second stirring system is arranged in the middle adjusting tank, and the second stirring system is used for stirring the separation liquid in the middle adjusting tank;
and the biological membrane advanced treatment system receives the separation liquid in the intermediate regulating tank and filters the separation liquid to form filtered water which is discharged.
Further, the biofilm advanced treatment system comprises:
the sedimentation tank is used for receiving separation liquid, and the separation liquid generates supernatant after being sedimentated by the sedimentation tank;
the biological filter is used for receiving supernatant in the sedimentation tank, the supernatant is precipitated in the biological filter to generate sludge and filtered water, the sludge flows into the regulating tank, and the filtered water is discharged after being treated in the oxidation pond.
Further, the garbage crusher also comprises a weighing device, wherein the weighing device is used for weighing the organic garbage, and the weighed organic garbage is conveyed to the crushing device.
The circulating vertical methane water heater uses methane as energy to generate hot water to provide heat for the regulating tank.
The solar heating system is characterized by further comprising a solar heating system, wherein the solar heating system is automatically started to automatically assist in heating the regulating reservoir through the temperature control sensing system when the temperature of the circulating vertical biogas water heater does not reach the set temperature, and the solar heating system is automatically stopped through the temperature control sensor when the temperature of the regulating reservoir reaches the set temperature.
Further, still include automatic lifting machine, automatic lifting machine promotes organic rubbish into reducing mechanism automatically.
To sum up, the utility model has the advantages that: 1. the process adopts a biodegradable organic garbage treatment technology, so that the power loss is small and the treatment effect is good; 2. the decomposed substances after degradation do not cause secondary pollution to underground water and soil; 3. the treated organic garbage is a natural organic fertilizer, the nutritive value in the organic fertilizer can improve the quality of crops, and the organic garbage is substantial for common people; 4. the byproduct methane generated in the fermentation process can be used as new energy, and the gas source can be recycled in a heating system of the process through a gas purification device, a gas-water separation device and a safe tempering device at present, and can also be used by peasant households, fruit and vegetable fresh-keeping, power generation and the like; 5. the system adopts equipment mainly comprising a fully-sealed anaerobic fermentation device and a high-efficiency three-phase separator; the anaerobic fermentation does not breed mosquitoes and flies, and the ground surface is clean and tidy, green and environment-friendly.
Drawings
FIG. 1 is a schematic view of the intelligent organic waste treatment system of the present invention;
FIG. 2 is a schematic diagram of a three-phase separation reactor;
FIG. 3 is a schematic diagram of the structure of a regulating reservoir;
FIG. 4 is a schematic structural view of an anaerobic fermentation chamber;
FIG. 5 is a schematic structural view of a heating tube;
FIG. 6 is a schematic structural diagram of a biofilm advanced treatment system;
FIG. 7 is a schematic diagram of an aerobic tank, a sedimentation tank and a biological filter;
fig. 8 is a floor plan of the organic waste treatment system.
Reference numerals: 1. a sludge bed; 2. an air chamber; 3. a settling zone; 4. a feed inlet of the adjusting tank; 5. a first stirring system; 6. a regulating tank; 7. an anaerobic fermentation bin; 8. heating a tube; 9. a feeding pipe at the bottom of the three-phase separation reactor; 10. an internal circulation system; 11. a slag discharge port; 12. air sealing; 13. an effluent weir; 14. a middle adjusting tank; 15. a lift pump; 16. an aerobic tank; 17. an internal reflux pump; 18. a reflux pump; 19. a sedimentation tank; 20. a biological filter; 21. biofilm filler; 22. an aeration pipe; 23. an air duct; 24. a sedimentation tank effluent weir; 25. a stabilizing barrel; 26. mounting a bracket; 27. a water inlet of the sedimentation tank; 28. a sedimentation tank sludge discharge pipe; 29. filtering a biological filter plate; 30. a water outlet of the biological filter; 31. a biological filter water distribution system; 32. a water inlet of the biological filter; 33. biogas.
Detailed Description
The embodiment of the novel intelligent organic waste treatment system of the present invention is further described with reference to fig. 1 to 8.
As shown in FIG. 1, a novel intelligent organic garbage disposal system comprises
The crushing device is used for crushing the organic garbage, after the organic garbage is crushed in multiple stages by the crusher, the surface area is increased after macromolecules are cut into micromolecules at high speed to form pasty fluid, and the organic garbage is quickly degraded;
the adjusting tank 6 is used for receiving the organic garbage in the crushing device, strains mixed with the organic garbage are added in the adjusting tank 6, a heating system and a first stirring system 5 are arranged in the adjusting tank 6, and under the working condition of set temperature, the organic garbage and the strains are alternately contacted with each other to achieve self reproduction of flora;
the anaerobic fermentation bin 7 is used for receiving a mixture of the organic garbage and the strains in the regulating tank 6, a first temperature control device and a second stirring system are arranged in the anaerobic fermentation bin 7, the temperature control device is used for controlling the temperature in the anaerobic bin, when the temperature exceeds or is lower than a set temperature, the heating system is automatically turned on or turned off, the second stirring system is used for stirring the mixture of the organic garbage and the strains, the contact area of the organic garbage and the strains is increased, the treatment capacity and the treatment effect are improved, methane, biogas slurry and biogas residues are generated, and the anaerobic fermentation bin 7 is arranged as a buried anaerobic fermentation bin;
the gas box is used for storing methane generated by the anaerobic fermentation bin 7;
the water collecting tank is used for receiving the liquid fermented by the anaerobic fermentation bin 7, and a second temperature control device is arranged in the water collecting tank and used for adjusting the temperature of the liquid in the water collecting tank so as to ensure the environment where microorganisms grow and inhabit;
the three-phase separation reactor is used for receiving and collecting liquid with the temperature adjusted in the water tank, uniformly discharging water under the distribution of the water distribution system, and generating anaerobic reaction in the process of contacting liquid and sludge particles through a sludge bed 1 containing granular sludge or flocculent sludge; the gas generated under anaerobic conditions induces internal circulation, which facilitates the formation and maintenance of granular sludge; some gas formed in the sludge layer is attached to sludge particles, the attached and unattached gas rises to the top of the three-phase separation reactor, the sludge rising to the surface impacts the bottom of a gas reflector of the three-phase separator to cause degassing of sludge flocs attached with bubbles, after the bubbles are released, the sludge particles are precipitated on the surface of a sludge bed 1, the gas is collected in a gas collection chamber 2 of the three-phase separator at the top of the three-phase separation reactor, water is discharged from the upper part of a precipitation zone 3, the three-phase separation reactor separates the liquid into slag, biogas 33 and separated liquid, the slag is discharged to an anaerobic fermentation chamber 7, and the biogas 33 is discharged to a gas tank;
the middle adjusting tank 14 is used for receiving the separation liquid separated by the three-phase separator, and a second stirring system is arranged in the middle adjusting tank 14 and is used for stirring the separation liquid in the middle adjusting tank 14;
and the biological film advanced treatment system receives the separated liquid in the intermediate regulating tank 14 and filters the separated liquid to form filtered water for discharge.
The biological film advanced treatment system comprises:
the sedimentation tank 19 is used for receiving the separation liquid, and the separation liquid is precipitated in the sedimentation tank 19 to generate a supernatant;
the biological filter 20 is used for receiving supernatant in the sedimentation tank 19, the supernatant is precipitated in the biological filter 20 to generate sludge and filtered water, the sludge flows into the regulating tank 6, and the filtered water is discharged after being treated in the oxidation pond.
The biomembrane depth system also comprises a biological chain type filler, an aeration device, a 3D biological rotating disc and a reflux device, and the system adopts A2An O process and a three-dimensional 3D biological rotating disc process are combined to form a deep water treatment process; through a novel complete treatment mode of anaerobic treatment, aerobic treatment, anaerobic treatment, backflow treatment, three-dimensional 3D biological rotating disc precipitation treatment, the biological filter 20 and the oxidation pond, biogas residues in the pond do not need to be cleaned and fished manually, only the residue cleaning equipment needs to be started periodically, and residue liquid is dried by the drying pond and can be used as an organic fertilizer after being directly washed and brushed according to multiplying power.
The system also comprises a weighing device which is used for weighing the organic garbage, conveying the weighed organic garbage to a crushing device, and setting the weighing device as a multifunctional intelligent scale, and a circulating vertical methane water heater which uses methane 33 as energy to generate hot water to provide heat for the regulating reservoir 6 so that materials reach the treatment effect, and then automatically controls the temperature and the equipment switch through a temperature control system in the reservoir to reasonably utilize resources; the automatic lifting machine automatically lifts the organic garbage into the crushing device; all electromechanical equipment, intelligent pipe valves and devices are displayed and transmitted in an intelligent management control system, and functions of the intelligent pipe valves and the intelligent pipe valves are combined through the Internet of things and the Internet.
As shown in fig. 1 and 7, the aerobic tank 16 is disposed between the intermediate adjusting tank 14 and the sedimentation tank 19, a biofilm filler 21 is disposed inside the aerobic tank 16, an air pipe 23 and an aeration pipe 22 are disposed at the bottom of the aerobic tank 16, a stabilizing barrel 25 is disposed at the upper portion of the sedimentation tank 19, a sedimentation tank water inlet 27 is disposed on the right side wall of the sedimentation tank 19, a sedimentation tank water outlet weir 24 is disposed on the left side wall of the sedimentation tank 19, a mounting bracket 26 is further disposed at the upper end of the sedimentation tank 19, a sedimentation tank sludge discharge pipe 28 is disposed at the lower portion of the sedimentation tank 19, a biofilter filter plate 29 is disposed at the lower portion of the biofilter 20, a biofilter water outlet 30 is disposed below the biofilter filter plate 29, a biofilter material is disposed above the biofilter filter plate 29, and a biofilter water inlet 32 and a.
The working principle is that as shown in figure 1, after the organic garbage passes through a multifunctional intelligent scale, is automatically weighed and uploads data, the organic garbage automatically enters a crusher to be crushed through an automatic lifting device, pasty materials automatically flow into a feed port 4 of an adjusting tank, water in a hot water tank is added into the adjusting tank 6, a heating system, a temperature control device and a first stirring system 5 are arranged in the adjusting tank 6, under the mutual cooperation of the heating system and the temperature control device, the adjusting tank 6 is kept at a set temperature to ensure the growth and the propagation of microbial flora, and simultaneously, the adjusting tank 6 is better contacted with the materials under the up-down turning circulation of the first stirring system 5, so that the uniform mixing effect of added strains and the materials is achieved, then the organic garbage enters an anaerobic fermentation bin 7 through a primary lifting pipe network and an automatic material distribution device, and the anaerobic fermentation bin 7 is made of glass fiber reinforced plastics according to the process requirements, the installation mode is a buried mode, in order to keep the material temperature balanced, a first temperature control device and a second stirring system are arranged in the anaerobic fermentation bin 7; under the unidirectional low-speed hydraulic propulsion of a second stirring system in the anaerobic fermentation bin 7, the mixture of the organic garbage and the strains is rapidly propagated by microbial flora and fully cuts macromolecules into micromolecules which are decomposed into methane, biogas slurry and biogas residues, and the methane is removed of hydrogen sulfide and peculiar smell through a gas tank, a collecting pipe and a gas purification device and enters a gas cabinet for storage; when clean energy is used, the flame is connected to a use place after passing through the safe tempering device, the gas-water separation device and the gas purification device, and the flame is returned to the sealed liquid level of the safe tempering water to automatically extinguish the flame source in order to prevent insufficient pressure in the tank; the liquid of the materials in the anaerobic fermentation chamber 7 after enough stay fermentation flows into a water collecting tank, a heating pipe 8 and a second temperature control device in the water collecting tank automatically adjust the set temperature of the liquid, the liquid with the adjusted temperature sends the liquid into a feeding pipe 9 at the bottom of a high-efficiency three-phase separation reactor through a high-pressure lift pump 15, an internal circulation system 10 is arranged in the three-phase separation reactor for periodic and timed circulation, a slag discharge port 11 is arranged at the bottom of the three-phase separation reactor and is discharged to the anaerobic fermentation chamber 7 at regular time, an air seal 12 and an air chamber 2 are arranged at the upper part, the separated marsh gas 33 enters the air chamber 2 and then enters an air cabinet through a gas collecting pipe for storage, the separated liquid is precipitated through a top water outlet hopper, an outlet weir 13 flows into a water outlet pipe to a middle adjusting tank 14, the separated liquid is homogenized through a second stirring system and then enters a biomembrane deep treatment system through a lift pump 15, and the supernatant, the precipitated sludge flows into the adjusting tank 6, and the effluent of the biological filter 20 is discharged after being treated in an oxidation pond.
It is above only the utility model discloses a preferred embodiment, the utility model discloses a scope of protection does not only confine above-mentioned embodiment, the all belongs to the utility model discloses a technical scheme under the thinking all belongs to the utility model discloses a scope of protection. It should be noted that, for those skilled in the art, various modifications and decorations can be made without departing from the principle of the present invention, and these modifications and decorations should also be regarded as the protection scope of the present invention.
Claims (8)
1. The utility model provides a novel intelligent organic refuse treatment system which characterized in that: the device comprises a crushing device, wherein the crushing device is used for crushing the organic garbage; the adjusting tank is used for receiving the organic garbage in the crushing device, strains mixed with the organic garbage are added in the adjusting tank, and a heating system and a first stirring system are arranged in the adjusting tank; the anaerobic fermentation bin is used for receiving a mixture of organic garbage and strains in the regulating reservoir, a first temperature control device and a second stirring system are arranged in the anaerobic fermentation bin, the first temperature control device is used for controlling the temperature in the anaerobic fermentation bin, and the second stirring system is used for stirring the mixture of the organic garbage and the strains to generate methane, biogas slurry and biogas residues; the gas tank is used for storing methane generated by the anaerobic fermentation bin; the water collecting tank is used for receiving the liquid fermented by the anaerobic fermentation bin, and a second temperature control device is arranged in the water collecting tank and used for adjusting the temperature of the liquid in the water collecting tank; the three-phase separation reactor is used for receiving and collecting liquid with the temperature adjusted in the water tank, the three-phase separation reactor separates the liquid into slag, methane and separation liquid, the slag is discharged to the anaerobic fermentation chamber, and the methane is discharged to the gas tank; the middle adjusting tank is used for receiving the separation liquid separated by the three-phase separation reactor, a second stirring system is arranged in the middle adjusting tank, and the second stirring system is used for stirring the separation liquid in the middle adjusting tank; and the biological membrane advanced treatment system receives the separation liquid in the intermediate regulating tank and filters the separation liquid to form filtered water which is discharged.
2. The novel intelligent organic waste treatment system according to claim 1, wherein: the biological film advanced treatment system comprises: the sedimentation tank is used for receiving separation liquid, and the separation liquid generates supernatant after being sedimentated by the sedimentation tank; the biological filter is used for receiving supernatant in the sedimentation tank, the supernatant is precipitated in the biological filter to generate sludge and filtered water, the sludge flows into the regulating tank, and the filtered water is discharged after being treated by the oxidation pond.
3. The novel intelligent organic waste treatment system according to claim 1, wherein: the garbage crusher further comprises a weighing device, wherein the weighing device is used for weighing the organic garbage, and the weighed organic garbage is conveyed to the crushing device.
4. The novel intelligent organic waste treatment system according to claim 1, wherein: still include automatic lifting machine, automatic lifting machine advances reducing mechanism with organic rubbish automatic lifting.
5. The novel intelligent organic waste treatment system according to claim 1, wherein: the anaerobic fermentation bin is made of glass fiber reinforced plastics.
6. The novel intelligent organic waste treatment system according to claim 1, wherein: and the methane enters the gas holder through the gas purification device to be stored.
7. The novel intelligent organic waste treatment system according to claim 1, wherein: and the liquid with the well-regulated temperature in the water collecting tank is sent into a feeding pipe at the bottom of the high-efficiency three-phase separation reactor through a lifting pump.
8. The novel intelligent organic waste treatment system according to claim 2, wherein: supernatant produced after the sedimentation in the sedimentation tank automatically flows to the biological filter through the height difference.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201921546166.8U CN210936404U (en) | 2019-09-17 | 2019-09-17 | Novel intelligent organic garbage treatment system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201921546166.8U CN210936404U (en) | 2019-09-17 | 2019-09-17 | Novel intelligent organic garbage treatment system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN210936404U true CN210936404U (en) | 2020-07-07 |
Family
ID=71370096
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201921546166.8U Active CN210936404U (en) | 2019-09-17 | 2019-09-17 | Novel intelligent organic garbage treatment system |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN210936404U (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2022052490A1 (en) * | 2020-09-12 | 2022-03-17 | 康保良 | Garbage treatment process and garbage treatment system |
-
2019
- 2019-09-17 CN CN201921546166.8U patent/CN210936404U/en active Active
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2022052490A1 (en) * | 2020-09-12 | 2022-03-17 | 康保良 | Garbage treatment process and garbage treatment system |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN103381420B (en) | Device and method for sewage collaborative reutilization comprehensive treatment | |
| CN110105095A (en) | A kind of innoxious and recycling processing method of kitchen garbage | |
| CN204550537U (en) | A kind of complete mixed biogas production system | |
| CN106957130B (en) | Treatment method of domestic sewage and organic solid waste | |
| CN103074381A (en) | Efficient resourceful treatment method through separation and anaerobic fermentation for kitchen waste | |
| JP2009532193A (en) | Devices, processes and systems for anaerobic digestion of sludge | |
| CN101337838A (en) | Combined anaerobic fermentation process for organic solid wastes | |
| CN102151683A (en) | Damp and heat fermentation comprehensive harmless and resource processing system for kitchen waste | |
| CN102212561B (en) | Processing method for fermenting straws in dry-process and wet-process combined way | |
| CN104263642B (en) | The integrated treatment unit of rubbish from cooking and excrement and urine water and treatment process | |
| CN107628736A (en) | A kind of livestock and poultry farm integration treatment for cow manure method | |
| CN104016556A (en) | Large-size waste recycling system | |
| CN104498532A (en) | Process for producing methane by mixing and fermenting organic wastes | |
| CN102502956B (en) | Municipal organic waste combined anaerobic treatment process and equipment | |
| CN210936404U (en) | Novel intelligent organic garbage treatment system | |
| CN103551367B (en) | Municipal living refuse comprehensive treatment method | |
| CN112517594A (en) | Environment-friendly intelligent organic garbage disposal system | |
| CN104789467B (en) | A kind of food garbage Anaerobic Digestion device | |
| CN210936405U (en) | Environment-friendly intelligent organic garbage disposal system | |
| CN208440534U (en) | Organic refuse treating system | |
| CN203140420U (en) | Organic garbage disposal system | |
| CN207581802U (en) | A kind of device of the mixed material fermentation and biogas production with hydro-thermal process | |
| CN103351059B (en) | System for producing marsh gas and fertilizer through cultivation waste water anaerobic treatment of domestic waste | |
| CN105180171A (en) | Garbage treatment method and garbage treatment equipment | |
| CN112517595A (en) | Novel intelligent organic garbage treatment system |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| GR01 | Patent grant | ||
| GR01 | Patent grant |