CN104961508B - Septic tank waste residue, which organises, utilizes treatment process - Google Patents

Septic tank waste residue, which organises, utilizes treatment process Download PDF

Info

Publication number
CN104961508B
CN104961508B CN201510344391.3A CN201510344391A CN104961508B CN 104961508 B CN104961508 B CN 104961508B CN 201510344391 A CN201510344391 A CN 201510344391A CN 104961508 B CN104961508 B CN 104961508B
Authority
CN
China
Prior art keywords
septic tank
waste residue
fermentation
tank waste
organises
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
Application number
CN201510344391.3A
Other languages
Chinese (zh)
Other versions
CN104961508A (en
Inventor
石伟
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.)
Qinghai Xiaomei Agricultural Technology Co.,Ltd.
Original Assignee
石伟
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 石伟 filed Critical 石伟
Priority to CN201510344391.3A priority Critical patent/CN104961508B/en
Publication of CN104961508A publication Critical patent/CN104961508A/en
Application granted granted Critical
Publication of CN104961508B publication Critical patent/CN104961508B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The present invention relates to a kind of septic tank waste residues to organise using treatment process, and septic tank waste residue is fermented, and the solid of septic tank waste residue and liquid after fermentation is separated, then isolated solid is sieved to, dried, is granulated and to obtain bio-organic fertilizer.The invention has the benefit that organising the present invention provides a kind of septic tank waste residue utilizes treatment process, waste residue in septic tank can be produced into bio-organic fertilizer, avoid pollution of the excrement to living environment, and bio-organic fertilizer is converted by excrement, reduce the use of chemical fertilizer, resource is not only saved in this way, and reduces the pollution of environment;Furthermore the physicochemical property that can improve soil by the bio-organic fertilizer that excrement converts, improves barren, hardened soil, and more nutritious healthier using the crops that this bio-organic fertilizer is planted.

Description

Septic tank waste residue, which organises, utilizes treatment process
Technical field
The present invention relates to sanitation equipments, and in particular to septic tank waste residue, which organises, utilizes treatment process.
Background technique
The problem of China human mortality is numerous, human feces high number, but the processing of excrement but becomes people's headache.Mesh Before, people generally take excrement is discharged directly into sewer and trade effluent to discharge into sewage treatment plant together and handle, but dirty Water treatment plant often can not separately handle industry or civilian rubbish when handling rubbish, handle to obtain through sewage plant in this way Sludge, quality just less than guarantee, is not used to agricultural planting, such as heavy metals exceeding standard.
On the other hand, in the rural area in China, chemical fertilizer is commonly used fertilizer, but chemical fertilizer is used for a long time and will cause soil Ground it is barren, hardened, influence whether the safety of national food for a long time.If the bio-organic fertilizer replacement converted with excrement Fertilizer can not only provide comprehensive nutrition for the growth of crops and can improve soil, it is therefore desirable to a kind of that excrement conversion is made a living The technique of organic fertilizer material protects environment in this way, can also improve soil.
Summary of the invention
In order to solve the above problems existing in the present technology, the present invention provides a kind of septic tank waste residues to organise at Septic tank waste residue is converted to bio-organic fertilizer by science and engineering skill.
The technical scheme adopted by the invention is as follows:
A kind of septic tank waste residue organises using treatment process, septic tank waste residue is fermented, by septic tank after fermentation The solid and liquid of waste residue are separated, then isolated solid is sieved to, dried, is granulated and to obtain bio-organic fertilizer. Entire fermentation process is sealing and continuous continual.
Preferably, probiotics is added in septic tank waste residue before fermentation, and stirs evenly, and the amount of added probiotics is septic tank 2/10000ths 4/10,000 of waste residue amount.Probiotics, which is added, facilitates the growth of beneficial bacterium, to be conducive to septic tank waste residue Fermentation.
Preferably, it is described fermentation be aerobic fermentation, the fermentation when it is 10-14 days a length of, ferment when, septic tank waste residue Fermentation temperature by room temperature, process one to two days fermentation calefactions are protected always to 50-60 DEG C, and hereafter in fermentation process The temperature is held, during the fermentation, first three days stir material every 6-8h, septic tank waste residue and oxygen can be made abundant in this way Contact, and be conducive to the growth of beneficial bacterium and the degradation of material.It was played from the 4th day the 9th day, stirs material every 12h; After 9th day, every stirring material for 24 hours.After aerobic fermentation, septic tank waste residue and probiotic group at material it is complete The full stench peculiar smell without at the beginning of starting, and it is changed into the breath with soil, not uncomfortable smell.
Preferably, liquid probiotic bacterium is added in septic tank waste residue after fermentation, and stirs evenly.Because of the process in fermentation In can generate heat, a part of probiotics may be killed, and supplement liquid probiotics, the amount of probiotics can be increased, can be made Septic tank waste residue is preferably degraded, and the flowing that liquid probiotic bacterium is conducive to septic tank waste residue is added, furthermore convenient for transfer.
Preferably, the probiotics is EM strain, and the liquid probiotic bacterium is EM bacterium solution.EM strain is by bifidocaterium, lactic acid The single cultures such as bacterium, photosynthetic bacteria, actinomyces are through special process fermentation, effectively compound microbial strain.
Preferably, isolated solid is subjected to anaerobic fermentation, nutritional ingredient is added after anaerobic fermentation and stirred equal It is even, then sieved again.Predominantly pyschrophile, mesophile participate in degradation during anaerobic fermentation.Because there is some probiotics to be Anaerobism probiotics can make septic tank produced by fermenting waste residues complete in this way, improve the quality of fermentation.It, can root when nutritional ingredient is added The amount of nutritional ingredient and the ingredient of nutritional ingredient are added according to the crops planted in different soils and soil, such as add nitrogen member Element, P elements etc., and stir evenly.
Preferably, the time of the anaerobic fermentation is 20-30 days.
Preferably, dry temperature is 60-80 DEG C, and the water content that septic tank waste residue is obtained after dry is its original water content 25-30%.
Preferably, be granulated bio-organic fertilizer partial size be 3-4mm.
Preferably, probiotics is added into the bio-organic fertilizer that granulation obtains, the amount for adding probiotics is biological organic The a ten thousandth of fertilizer total weight, it is to be mixed uniformly after packed.Because high temperature can be generated during granulation, high temperature is removed Outside strain, the strains such as other medium temperatures have different degrees of loss, in order to guarantee the amount of bacterium colony group number in bio-organic fertilizer, into And guarantee the quality of bio-organic fertilizer, probiotics is added before encapsulation.
Preferably, the bio-organic fertilizer after packaging reuses after should saving 10-20 days, such bio-organic fertilizer Using effect can be more preferably.
Preferably, the liquid being separated after fermentation is recycled, it, after processing can be with because being also enriched in nutrition in liquid It is used as nutrient solution.
Preferably, the exhaust gas generated during production bio-organic fertilizer is collected with the mode of negative pressure, because of production The primary waste gases generated during bio-organic fertilizer are ammonias, and the characteristic of water is highly soluble in using ammonia, is collected with water And prepare the nutrient solution for being rich in nitrogen.
Preferably, the septic tank waste residue organise using treatment process by septic tank waste residue organise all-in-one machine implement, The septic tank waste residue all-in-one machine that organises includes that mixing plant, aerobic fermentation equipment, solid-liquid separating equipment, anaerobic fermentation are set Standby, screening plant, drying equipment, Granulation Equipments and packaging facilities, it is the mixing plant, the aerobic fermentation equipment, described solid Liquid separation equipment, the anaerobic fermentation equipment, the screening plant, the drying equipment, the Granulation Equipments and the packaging Equipment passes sequentially through pipeline connection.
The invention has the benefit that the present invention provides a kind of septic tank waste residues to organise using treatment process, can incite somebody to action Waste residue in septic tank is produced into bio-organic fertilizer, avoids pollution of the excrement to living environment, and convert excrement to Bio-organic fertilizer reduces the use of chemical fertilizer, not only saves resource in this way, and reduces the pollution of environment;Furthermore by excrement Just the bio-organic fertilizer converted can improve the physicochemical property of soil, improve barren, hardened soil, and use this life The crops of organic fertilizer material plantation are more nutritious healthier.
Specific embodiment
Below with reference to embodiment, the invention will be further described.
Embodiment 1
A kind of septic tank waste residue organises using treatment process, and septic tank waste residue is added in mixing plant, is then added The EM strain of septic tank waste residue weight 2/10000ths, is transported in installation for fermenting again after stirring and ferments, and this time ferments For aerobic fermentation, fermentation when it is 10 days a length of.
In fermentation, the fermentation temperature of septic tank waste residue is by room temperature, by one day fermentation calefaction to 50 DEG C, and Hereafter the temperature is always maintained in fermentation process.In order to guarantee that septic tank waste residue and oxygen come into full contact with, it is useless to accelerate septic tank The degradation of slag, during fermentation, first three days stir material every 6h, play from the 4th day the 9th day and turn over every 12h Make a movement material, stirs material again when fermenting and completing.
Because that can generate heat during fermentation, the temperature in installation for fermenting can be increased, and may kill a part of EM Septic tank waste residue weight a ten thousandth EM bacterium solution is added into the septic tank waste residue after fermentation for the amount for guaranteeing EM strain for strain, The flowing that EM bacterium solution is conducive to septic tank waste residue is added, facilitates transfer.Septic tank waste residue is separated by solid-liquid separation again.
Because some in EM strain is anaerobism probiotics, to make septic tank produced by fermenting waste residues improve the quality of fermentation completely, The anaerobic fermentation that isolated solid is carried out to 20 days, according to the agriculture planted in different soil and soil after anaerobic fermentation Crop adds the amount of nutritional ingredient and the ingredient of nutritional ingredient, such as nitrogen, P elements, and stirs evenly.
The septic tank waste residue that nutritional ingredient is added is sieved with the sieve of 4 mesh, and by large-sized septic tank waste residue It is crushed, the water content then dried under conditions of 60 DEG C into septic tank waste residue is the 30% of its original water content.So It carries out being granulated the partial size 3mm for making gained bio-organic fertilizer again afterwards.Probiotics is added into resulting bio-organic fertilizer again, Add probiotics amount be bio-organic fertilizer total weight a ten thousandth, it is to be mixed uniformly after packed.Because in granulation High temperature can be generated in the process, in addition to high-temperature strain, the strains such as other medium temperatures have different degrees of loss, and in order to guarantee biology The amount of bacterium colony group number, guarantees the quality of bio-organic fertilizer, probiotics is added before encapsulation in organic fertilizer.
Using effect in order to make bio-organic fertilizer more preferably makes behind bio-organic fertilizer storage 10 days after packaging again With.
In order to make septic tank waste residue maximize the use, discharge amount is dropped to during producing bio-organic fertilizer Minimum recycles the liquid separated after fermentation, and nutritious because containing in its liquid, can be used as nutrient solution after processing makes With;In addition the exhaust gas generated during production bio-organic fertilizer is collected with the mode of negative pressure, because producing biological organic The primary waste gases generated during fertilizer are ammonias, and the characteristic of water is highly soluble in using ammonia, is collected with water and is used to make The standby nutrient solution for being rich in nitrogen.
Embodiment 2
On the basis of embodiment 1, septic tank waste residue is added in mixing plant, septic tank waste residue weight ten thousand is then added / tri- EM strain, aerobic fermentation when it is 12 days a length of, fermentation when septic tank waste residue fermentation temperature by room temperature, warp The fermentation calefaction for spending one day is to 55 DEG C, and during the fermentation, first three days stir material every 7h, plays the 9th from the 4th day It stirs material every 12h, after the 9th day, every stirring material for 24 hours.
To make septic tank produced by fermenting waste residues improve the quality of fermentation completely, the anaerobic that isolated solid carries out 25 days is sent out Ferment.
With the sieve of 6 mesh to be added nutritional ingredient septic tank waste residue sieve, by the big septic tank waste residue of partial size into Row crushes, and the water content then dried under conditions of 70 DEG C into septic tank waste residue is the 27% of its original water content.Then It carries out being granulated the partial size 3.5mm for making gained bio-organic fertilizer again.
Using effect in order to make bio-organic fertilizer more preferably makes behind bio-organic fertilizer storage 15 days after packaging again With.
Embodiment 3
On the basis of embodiment 1, septic tank waste residue is added in mixing plant, septic tank waste residue weight ten thousand is then added / tetra- EM strain, aerobic fermentation when it is 14 days a length of, fermentation when septic tank waste residue fermentation temperature by room temperature, warp Fermentation calefaction two days later is to 60 DEG C, and during the fermentation, first three days stir material every 8h, plays the 9th from the 4th day It stirs material every 12h, after the 9th day, every stirring material for 24 hours.
To make septic tank produced by fermenting waste residues improve the quality of fermentation completely, the anaerobic that isolated solid carries out 30 days is sent out Ferment.
With the sieve of 6 mesh to be added nutritional ingredient septic tank waste residue sieve, by the big septic tank waste residue of partial size into Row crushes, and the water content then dried under conditions of 80 DEG C into septic tank waste residue is the 25% of its original water content.Then It carries out being granulated the partial size 4mm for making gained bio-organic fertilizer again.
Using effect in order to make bio-organic fertilizer more preferably makes behind bio-organic fertilizer storage 20 days after packaging again With.
The present invention is not limited to above-mentioned preferred forms, anyone can show that other are various under the inspiration of the present invention The product of form, however, make any variation in its shape or structure, it is all that there is skill identical or similar to the present application Art scheme, is within the scope of the present invention.

Claims (6)

1. a kind of septic tank waste residue, which organises, utilizes treatment process, it is characterised in that: septic tank waste residue 2/10000ths-is added very much Four probiotics after, by septic tank waste residue carry out aerobic fermentation, the solid of septic tank waste residue and liquid after fermentation are divided From, then by isolated solid progress anaerobic fermentation, bio-organic fertilizer is sieved, dried, is granulated and to obtain after fermentation;
The probiotics is EM strain;
The septic tank waste residue organises uninterruptedly to be carried out under air-proof condition using processing;
A length of 10-14 days when the aerobic fermentation, during the fermentation, the fermentation temperature of septic tank waste residue is by room temperature, warp The fermentation calefaction for spending one to two days is to 50-60 DEG C, and first three days of fermenting are every 6-8h turning over materials;4th day to the 9th day, every 12h turning over materials;After 9th day, every turning over materials for 24 hours;
The drying temperature is 60-80 DEG C, and the water content that material is obtained after dry is the 25-30% of material gross weight;
The septic tank waste residue, which organises, to be implemented using treatment process by the septic tank waste residue all-in-one machine that organises, and the septic tank is useless Slag organise all-in-one machine include mixing plant, it is aerobic fermentation equipment, solid-liquid separating equipment, anaerobic fermentation equipment, screening plant, dry Dry equipment, Granulation Equipments and packaging facilities, it is the mixing plant, the aerobic fermentation equipment, the solid-liquid separating equipment, described Anaerobic fermentation equipment, the screening plant, the drying equipment, the Granulation Equipments and the packaging facilities pass sequentially through pipeline Connection.
2. septic tank waste residue, which organises, according to claim 1 utilizes treatment process, it is characterised in that: change excrement after fermentation Liquid probiotic bacterium is added in the waste residue of pond, and stirs evenly.
3. septic tank waste residue, which organises, according to claim 1 utilizes treatment process, it is characterised in that: consolidate isolated Body carries out anaerobic fermentation, and nutritional ingredient is added after anaerobic fermentation and stirs evenly, is then sieved again.
4. septic tank waste residue, which organises, according to claim 3 utilizes treatment process, it is characterised in that: the anaerobic fermentation Time is 20-30 days.
5. septic tank waste residue, which organises, according to claim 1 utilizes treatment process, it is characterised in that: be granulated to obtain biological organic The partial size of fertilizer is 3-4mm.
6. septic tank waste residue, which organises, according to claim 1 utilizes treatment process, it is characterised in that: the life obtained to granulation Probiotics is added in organic fertilizer material, the amount for adding probiotics is a ten thousandth of bio-organic fertilizer total weight, to be mixed equal It is packed after even.
CN201510344391.3A 2015-06-19 2015-06-19 Septic tank waste residue, which organises, utilizes treatment process Active CN104961508B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510344391.3A CN104961508B (en) 2015-06-19 2015-06-19 Septic tank waste residue, which organises, utilizes treatment process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510344391.3A CN104961508B (en) 2015-06-19 2015-06-19 Septic tank waste residue, which organises, utilizes treatment process

Publications (2)

Publication Number Publication Date
CN104961508A CN104961508A (en) 2015-10-07
CN104961508B true CN104961508B (en) 2019-02-22

Family

ID=54215636

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510344391.3A Active CN104961508B (en) 2015-06-19 2015-06-19 Septic tank waste residue, which organises, utilizes treatment process

Country Status (1)

Country Link
CN (1) CN104961508B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108218480A (en) * 2017-12-25 2018-06-29 石伟 A kind of method and its system for handling human excrement
CN112607936A (en) * 2020-11-26 2021-04-06 苏州聚隆环保科技有限公司 Sewage treatment process

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101307332A (en) * 2008-06-23 2008-11-19 昆明东燃科技开发有限公司 Innocent comprehensive approach method for human feces by biotechnology
CN202187001U (en) * 2011-07-12 2012-04-11 浏阳市天恩生物科技有限公司 Outdoor system for cycling, fermenting and treating feces and urine from livestock and poultry farm
CN102874996A (en) * 2011-07-12 2013-01-16 浏阳市天恩生物科技有限公司 Recovery and reutilization process of excrement and urine in livestock and poultry farm
CN103265154A (en) * 2013-04-27 2013-08-28 罗炳 Resource utilization and comprehensive treatment process for sewage and manure generated during cultivation
CN103351092A (en) * 2013-07-29 2013-10-16 郭金陵 Method and equipment for harmlessly treating and utilizing livestock feces on large-scale livestock farm
CN104628436A (en) * 2015-02-14 2015-05-20 张仲元 Method and device for preparing organic fertilizer by utilizing fecal sewage in urban septic tank

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101307332A (en) * 2008-06-23 2008-11-19 昆明东燃科技开发有限公司 Innocent comprehensive approach method for human feces by biotechnology
CN202187001U (en) * 2011-07-12 2012-04-11 浏阳市天恩生物科技有限公司 Outdoor system for cycling, fermenting and treating feces and urine from livestock and poultry farm
CN102874996A (en) * 2011-07-12 2013-01-16 浏阳市天恩生物科技有限公司 Recovery and reutilization process of excrement and urine in livestock and poultry farm
CN103265154A (en) * 2013-04-27 2013-08-28 罗炳 Resource utilization and comprehensive treatment process for sewage and manure generated during cultivation
CN103351092A (en) * 2013-07-29 2013-10-16 郭金陵 Method and equipment for harmlessly treating and utilizing livestock feces on large-scale livestock farm
CN104628436A (en) * 2015-02-14 2015-05-20 张仲元 Method and device for preparing organic fertilizer by utilizing fecal sewage in urban septic tank

Also Published As

Publication number Publication date
CN104961508A (en) 2015-10-07

Similar Documents

Publication Publication Date Title
CN101544959B (en) Complex probiotics for environmental remediation, preparation method and application thereof
CN100387551C (en) Method of producing active nutritional fertilizer using old domostic garbage
CN103044138B (en) Preparation method for composite biological bacterial fertilizer
CN101913933B (en) Method for producing organic complex fertilizer through microbial solid fermentation
RU2322427C1 (en) Method of biologically processing bird dung
CN106497836A (en) A kind of complex micro organism fungicide of fermented stalk and its preparation method and application
CN104326774B (en) The method that the fermentation animal wastes of a kind of microorganism fluid fertilizer convert organic granular fertilizer
CN106135884B (en) Utilize agricultural wastes produced environment friendly function ferment and preparation method thereof
CN105384534B (en) A kind of liquid organic biofertilizer and preparation method thereof
Zhang et al. Algal sludge from Taihu Lake can be utilized to create novel PGPR-containing bio-organic fertilizers
CN106748420A (en) The method that biological organic fertilizer is processed using earthworm
CN105349471A (en) Preparation method of microbial flora preparation and application thereof
CN106734184A (en) A kind of in-situ remediation method of heavy-metal contaminated soil
CN105084957A (en) Method for preparing bio-organic fertilizer from filter residues produced after anaerobic fermentation of kitchen waste and application of bio-organic fertilizer
Hoe et al. Recycling of oil palm empty fruit bunch as potential carrier for biofertilizer formulation
CN105638399A (en) Functional type soilless culture substrate using mushroom dreg and biogas residue as raw material
CN111793656A (en) Treatment method of agricultural organic waste
CN104926535A (en) Spirulina peptide bio-organic fertilizer
CN104642530A (en) Comprehensive utilization method for enteromorpha prolifera
Lu et al. From manure to high-value fertilizer: The employment of microalgae as a nutrient carrier for sustainable agriculture
SE450769B (en) PROCEDURE AND PLANT FOR USE OF WASTE PRODUCTS FROM WASTE
CN112125712A (en) Garbage treatment method
CN207862214U (en) The device of biological organic fertilizer is prepared using pig breeding waste
CN104961610A (en) Soil conditioner and use method thereof
CN104961508B (en) Septic tank waste residue, which organises, utilizes treatment process

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20190709

Address after: 810000 Room 242, No. 1, Hutai West Lane, Chengxi District, Xining City, Qinghai Province

Patentee after: Shi Yu

Address before: 810000 Room 452, Building 5, No. 12, Yuanshu Lane, Chengxi District, Xining City, Qinghai Province

Patentee before: Shi Wei

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20210914

Address after: 810000 room 242, No. 1, Hutai West Lane, Chengxi District, Xining City, Qinghai Province

Patentee after: Shi Yu

Patentee after: Qinghai Xiaomei Agricultural Technology Co.,Ltd.

Address before: 810000 room 242, No. 1, Hutai West Lane, Chengxi District, Xining City, Qinghai Province

Patentee before: Shi Yu

TR01 Transfer of patent right