CN108641921A - A kind of domestic organic garbage processing system and method - Google Patents

A kind of domestic organic garbage processing system and method Download PDF

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Publication number
CN108641921A
CN108641921A CN201810793807.3A CN201810793807A CN108641921A CN 108641921 A CN108641921 A CN 108641921A CN 201810793807 A CN201810793807 A CN 201810793807A CN 108641921 A CN108641921 A CN 108641921A
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pond
anaerobic fermentation
tank
retort
garbage processing
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骆泽科
骆宣权
周苏谊
余肖彪
陈炜
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Zhuji Lv Jing Energy Saving And Environmental Protection Technology Co Ltd
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Zhuji Lv Jing Energy Saving And Environmental Protection Technology Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M21/00Bioreactors or fermenters specially adapted for specific uses
    • C12M21/04Bioreactors or fermenters specially adapted for specific uses for producing gas, e.g. biogas
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M23/00Constructional details, e.g. recesses, hinges
    • C12M23/36Means for collection or storage of gas; Gas holders
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    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M27/00Means for mixing, agitating or circulating fluids in the vessel
    • C12M27/02Stirrer or mobile mixing elements
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M41/00Means for regulation, monitoring, measurement or control, e.g. flow regulation
    • C12M41/12Means for regulation, monitoring, measurement or control, e.g. flow regulation of temperature
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    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M45/00Means for pre-treatment of biological substances
    • C12M45/02Means for pre-treatment of biological substances by mechanical forces; Stirring; Trituration; Comminuting
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12MAPPARATUS FOR ENZYMOLOGY OR MICROBIOLOGY; APPARATUS FOR CULTURING MICROORGANISMS FOR PRODUCING BIOMASS, FOR GROWING CELLS OR FOR OBTAINING FERMENTATION OR METABOLIC PRODUCTS, i.e. BIOREACTORS OR FERMENTERS
    • C12M45/00Means for pre-treatment of biological substances
    • C12M45/04Phase separators; Separation of non fermentable material; Fractionation

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Abstract

The invention discloses a kind of domestic organic garbage processing system and methods, including sequentially connected grinding device, equipment for separating liquid from solid, hydrolization and acidification tank, intermediate connection pool, anaerobic fermentation tank, water pressure chamber, the fertile pond of storage, inspection shaft, aerobic treatment pond, sedimentation basin, artificial swamp and outer row pond, domestic organic garbage is through crushing, after separation of solid and liquid, again through hydrolysis acidification, anaerobic fermentation, storage fertilizer, aerobic treatment, discharge up to standard after precipitation, the present invention has energy-efficient, Economization on land, harmless treatment, ecology is disposed, epidemic prevention diseases prevention, circular economy, recycling, construction period is short, the advantages that safe and reliable.

Description

A kind of domestic organic garbage processing system and method
Technical field
The present invention relates to domestic organic garbage processing system and methods.
Background technology
As economy, population grow continuously and fast, garbage disposal, which has become, influences environmental protection, resident living and can The important topic of sustainable development, house refuse not only pollute environment, destroy beautiful rural area, also spread the disease, threaten the mankind and The harmonious coexistence of the Nature, resolving the process problem of house refuse is particularly important.
Several years ago, the processing mode of China's organic waste is mainly sanitary landfills, burning, compost etc., and no matter which kind of is handled Mode has respective limitation:1, sanitary landfills takes up a large area, soil, underground water and air all can be polluted and be dived Harm;2, burn that high for organic waste moisture content, calorific value amount is low, when burning causes the significant wastage of resource and burning It is also easy to produce bioxin in the process, secondary pollution and greatly harm are formed to the mankind;3, aerobic compost is a kind of energy consumption process, is needed It wants input energy to supplement, while needing the energy and manual operation, finally reach treatment effect.
Invention content
Present invention aims to overcome that above-mentioned the deficiencies in the prior art, provide a kind of more environmentally-friendly organic rubbish of reliably living Rubbish processing system and method.
The technical scheme is that:A kind of domestic organic garbage processing system, including it is sequentially connected grinding device, solid Liquid separating apparatus, hydrolization and acidification tank, intermediate connection pool, anaerobic fermentation tank, the fertile pond of storage, aerobic treatment pond, artificial swamp and Outer row pond is designed with heating temperature-controlled stirring equipment, slag-draining device and collecting methane in the hydrolization and acidification tank and anaerobic fermentation tank Pipe, the collecting methane pipe pass sequentially through air accumulator and gas holder and are connected with downstream gas equipment, on the hydrolization and acidification tank also Equipped with Manual material feeding mouth, it is additionally provided with water pressure chamber between the anaerobic fermentation tank and the fertile pond of storage, at the storage fertilizer pond and aerobic biochemical Reason is additionally provided with inspection shaft between pond, and sedimentation basin is additionally provided between the aerobic treatment pond and artificial swamp.
Further, the air accumulator periphery is additionally provided with warning device, desulfurization dewatering device and flame-retardant device.
Further, the heating temperature-controlled stirring equipment is made of heating tube, hydraulic agitation device and temperature probe.
Further, the hydrolysis acidification retort, anaerobic fermentation retort, the fertile pond of storage, desulfurization dewatering device, fire-retardant Device, aerobic treatment pond and artificial swamp are that stainless steel, fiberglass or synthetic material are made at molding.
Further, the hydrolization and acidification tank, intermediate connection pool, anaerobic fermentation tank and water pressure chamber are embedded in underground.
Further, further include a cycle fireplace, described cycle fireplace one end is connected with the flame-retardant device and gas holder, institute The cycle fireplace other end is stated by heat pump to be connected with the heating temperature-controlled stirring equipment.
Further, the fertile pond of the storage is additionally provided with hand hoisting equipment.
A kind of domestic organic garbage processing method, includes the following steps:
Step 1: organic waste inputs hydrolysis acidification retort, hydrolysis acidification reaction by crushing, being separated by solid-liquid separation by pipeline Tank, which matches to add, suitable biological inoculum, and suitable temperature is kept in hydrolysis acidification retort under heating temperature-controlled stirring equipment cooperation, Ensure to tie up the place that biological flora own growth is bred, meanwhile, heating temperature-controlled stirring equipment stirs object in agitation pond up and down makes it It mutually better contacts with, to achieve the effect that hydrolysis acidification;
Step 2: the organic waste through hydrolysis acidification through intermediate connection pool flow into anaerobic fermentation retort, fermentation 60 to 80 days, anaerobic fermentation retort is interior to have bio anaerobic strain, anaerobic fermentation retort to match in heating temperature-controlled stirring equipment with throwing Make to keep suitable temperature in pond under conjunction, it is ensured that the place of dimension biological flora own growth breeding, meanwhile, heat temperature-controlled stirring equipment Stirring object in agitation pond up and down makes it mutually better contact with, and organic waste is fully decomposed into methane, biogas slurry and biogas residue;
Step 4: organic waste is through after fully, liquid flows into the fertile pond of water pressure chamber flow direction storage in anaerobic fermentation retort Carry out storage fertilizer;
Step 5: the waste liquid after storage fertilizer uses the processing mode that is combined of A2O techniques and SBR techniques, through precipitation, anaerobism, Aerobic, precipitation, is discharged at reflux again after the processing of artificial swamp oxidation pond is up to standard.
Further, in step 2, methane enters air accumulator by desulfurizer and stores, when using process of methane, biogas Field of employment is accessed again by fire-retarding device, and to prevent pressure inside the tank insufficient, flare string is back at flame-retardant device water level, automatic distinguishing Kindling material.
The beneficial effects of the invention are as follows:
It is energy-efficient;
Economization on land:The system body equipment is buried, and earth's surface can plant crop and afforest and beautify the environment;
Harmless treatment:Decomposition product after degradation does not pollute underground water and ground water generation again;
Ecology is disposed:Earth's surface is clean and tidy, does not grow mosquitos and flies, environmentally protective;
Epidemic prevention diseases prevention:Organic waste has killed a large amount of poisonous and harmful bacterium after Anaerobic Treatment, reduces disease and passes It broadcasts, ensures people's health;
Circular economy:Rubbish is the treasured mislayed, and organic waste is a kind of natural organic fertilizer after treatment, its inside Nutritive value crops quality can be improved, allow peasant to receive more tangible benefits;
Recycling:The byproduct methane gas of generation, can make new energy use, it is possible to provide to peasant household, preserving fruit and vegetable utilizing, Or it is recycled on website;
It is intelligent:Using network remote monitoring, manage and protect precisely, management cost is low, efficient;
Construction period is short:Easy for construction, operating cost is relatively low, Virtual production, quality assurance and has a safety feature;
Securely and reliably:Configure fire-retarding device, desulfurizer and water pressure chamber, automatic decompression design and website gas leakage warning System, it is more safer than septic tank.
Description of the drawings
Fig. 1 is the structural schematic diagram of the present invention;
Fig. 2 is the structural schematic diagram that the present invention is embedded under ground portion;
Fig. 3 is the process flow chart of the present invention.
Specific implementation mode
Below with reference to the embodiments and with reference to the accompanying drawing the technical solutions of the present invention will be further described.
In conjunction with shown in Fig. 1 and Fig. 2, a kind of domestic organic garbage processing system, including it is sequentially connected grinding device 1, solid Liquid separating apparatus, hydrolization and acidification tank 2, intermediate connection pool 3, anaerobic fermentation tank 4, the fertile pond 5 of storage, aerobic treatment pond 6, Manual moist Ground 7 and outer row pond 8 are designed with heating temperature-controlled stirring equipment, 9 and of slag-draining device in the hydrolization and acidification tank 2 and anaerobic fermentation tank 4 Collecting methane pipe 10, the collecting methane pipe 10 passes sequentially through air accumulator 11 and gas holder 12 is connected with downstream gas equipment, institute It states and is additionally provided with Manual material feeding mouth 13 on hydrolization and acidification tank 2, water pressure chamber 14 is additionally provided between the anaerobic fermentation tank 4 and storage fertilizer pond 5, It is additionally provided with inspection shaft 15, the aerobic treatment pond 6 and artificial swamp 7 between the fertile pond 5 of the storage and aerobic biochemical treatment tank 6 Between be additionally provided with sedimentation basin 16.
Further, warning device, desulfurization dewatering device 18 and flame-retardant device 19 are additionally provided in the air accumulator 11.
Further, the heating temperature-controlled stirring equipment is by 22 groups of heating tube 20, hydraulic agitation device 21 and temperature probe At.
Further, the hydrolysis acidification retort 2, anaerobic fermentation retort 4, the fertile pond 5 of storage, desulfurization dewatering device 18, Flame-retardant device 19, aerobic treatment pond 6 and artificial swamp 7 are that stainless steel, fiberglass or synthetic material are made at molding.
Further, the hydrolization and acidification tank 2, intermediate connection pool 3, anaerobic fermentation tank 4 and water pressure chamber 14 are embedded in underground.
Further, further include a cycle fireplace 23, described 23 one end of cycle fireplace and 12 phase of the flame-retardant device and gas holder Connection, 23 other end of cycle fireplace are connected by heat pump with the heating temperature-controlled stirring equipment.
Further, storage fertilizer pond 5 is additionally provided with hand hoisting equipment.
A kind of domestic organic garbage processing method, as shown in figure 3, organic waste by leading portion classification disposition after, from crushing And it is directly entered hydrolysis acidification retort from pipe network after equipment for separating liquid from solid processing, it is continuously added to according to disposition capacity, hydrolysis acid Change to match in retort and add suitable biological inoculum, under the effect of strain self-reproduction, the phase interworking of hydraulic mixing and temperature Under conjunction, macromolecular is decomposed into small molecule, enters anaerobic fermentation retort using intermediate connection pool;
The technique divides three phases:First stage is hydrolysis acidification, and temperature is controlled in retort, and pH value, waterpower are stirred It mixes speed, material and flora is allowed to contact with each other, macromolecular is decomposed into small molecule, to improve follow-up anaerobic fermentation retort Effect;Second stage is anaerobic fermentation, and equipment, heating system, temperature probe, the hydraulic mixing system of retort configuration are being set Determine in range, interaction by small organic molecule under the interaction of bio anaerobic flora and equipment, be converted into methane gas, liquid and Slag;Methane gas enters air accumulator by desulfurizer by collection system pipeline and collects, and the gas after collection passes through fire-retardant Device can access field of employment and be used as new energy.Using before gas by desulfurizer internal oxidition iron under the action of, remove Devulcanization hydrogen and other peculiar smell access field of employment in gas tank when gas use by flame-retardant device;
There is flare time string in gas pressure inside the tank deficiency in order to prevent, and spy is equipped with fire-retarding device, dress before accessing field of employment Automatic distinguishing kindling material after thering is water level not necessarily, tempering to go here and there back in setting;
Liquid injection water pressure chamber, flow direction storage are fertile after the residence time of setting fully ferments in anaerobic fermentation retort Pond;
Gas pressure in retort is maintained in water pressure chamber, that is, is reacted pressure inside the tank and increased, and water pressure chamber water level rises, Otherwise to decline, it is ensured that gas phase keeps the numerical value of design homeostasis in retort;
Storage fertile pond is equipped with hand hoisting equipment when zymotic fluid being taken to make organic fertilizer on material taking mouth, pours and makees convenient for common people Object;
Waste liquid after storage fertilizer uses the processing mode that is combined of A2O techniques and SBR techniques, through precipitation, anaerobism, aerobic, heavy It forms sediment, reflux, discharged again after the processing of artificial swamp oxidation pond is up to standard;
Biogas residue is equipped with cleaning dregs system in pond, is dragged for clearly without manually entering pond, it is only necessary to periodically turn on scarfing cinder equipment, slag liquid is through overdrying After changing pond desiccation, used as organic fertilizer while can also soil improvement.
It should be noted that when element is referred to as " being fixed on " another element, it can be directly on another element Or there may also be elements placed in the middle.When an element is considered as " connection " another element, it can be directly connected to To another element or it may be simultaneously present centering elements.Term as used herein " vertical ", " horizontal ", " left side ", " right side " and similar statement for illustrative purposes only, are not offered as being unique embodiment.
Unless otherwise defined, all of technologies and scientific terms used here by the article and belong to the technical field of the present invention The normally understood meaning of technical staff is identical.Used term is intended merely to description tool in the description of the invention herein The purpose of the embodiment of body, it is not intended that in the limitation present invention.Term " and or " used herein includes one or more Any and all combinations of relevant Listed Items.
The foregoing is merely illustrative of the preferred embodiments of the present invention, is not intended to limit the invention, all essences in the present invention With within principle, any modification, equivalent replacement, improvement and so on should all be included in the protection scope of the present invention god.

Claims (9)

1. a kind of domestic organic garbage processing system, it is characterised in that:Including sequentially connected grinding device, it is separated by solid-liquid separation dress It sets, hydrolization and acidification tank, intermediate connection pool, anaerobic fermentation tank, store up fertile pond, aerobic treatment pond, artificial swamp and outer row pond, institute It states and is designed with heating temperature-controlled stirring equipment, slag-draining device and collecting methane pipe, the natural pond in hydrolization and acidification tank and anaerobic fermentation tank Gas collecting pipe passes sequentially through air accumulator and gas holder and is connected with downstream gas equipment, and artificial throwing is additionally provided on the hydrolization and acidification tank Material mouth is additionally provided with water pressure chamber, between the fertile pond of the storage and aerobic biochemical treatment tank also between the anaerobic fermentation tank and the fertile pond of storage Equipped with inspection shaft, sedimentation basin is additionally provided between the aerobic treatment pond and artificial swamp.
2. a kind of domestic organic garbage processing system according to claim 1, it is characterised in that:The air accumulator periphery is also Equipped with warning device, desulfurization dewatering device and flame-retardant device.
3. a kind of domestic organic garbage processing system according to claim 1, it is characterised in that:The heating temperature control stirring Device is made of heating tube, hydraulic agitation device and temperature probe.
4. a kind of domestic organic garbage processing system according to claim 2, it is characterised in that:The hydrolysis acidification reaction Tank, anaerobic fermentation retort, the fertile pond of storage, desulfurization dewatering device, flame-retardant device, aerobic treatment pond and artificial swamp are stainless Steel, fiberglass or synthetic material are made at molding.
5. a kind of domestic organic garbage processing system according to claim 1, it is characterised in that:The hydrolization and acidification tank, Intermediate connection pool, anaerobic fermentation tank and water pressure chamber are embedded in underground.
6. a kind of domestic organic garbage processing system according to claim 1, it is characterised in that:It further include a cycle wall Stove, described cycle fireplace one end are connected with the flame-retardant device and gas holder, the cycle fireplace other end by heat pump with it is described Heating temperature-controlled stirring equipment is connected.
7. a kind of domestic organic garbage processing system according to claim 1, it is characterised in that:The fertile pond of the storage is additionally provided with Hand hoisting equipment.
8. a kind of domestic organic garbage processing method, which is characterized in that include the following steps:
Step 1: organic waste inputs hydrolysis acidification retort by crushing, being separated by solid-liquid separation by pipeline, hydrolysis acidification retort is matched Adding has suitable biological inoculum, and suitable temperature is kept in hydrolysis acidification retort under heating temperature-controlled stirring equipment cooperation, it is ensured that The place of biological flora own growth breeding is tieed up, meanwhile, heating temperature-controlled stirring equipment stirs object in agitation pond up and down makes its phase more It contacts well, to achieve the effect that hydrolysis acidification;
Step 2: the organic waste through hydrolysis acidification flows into anaerobic fermentation retort, fermentation 60 to 80 through intermediate connection pool It has bio anaerobic strain in anaerobic fermentation retort with throwing, and anaerobic fermentation retort is under heating temperature-controlled stirring equipment cooperation Make to keep suitable temperature in pond, it is ensured that the place of dimension biological flora own growth breeding, meanwhile, heat temperature-controlled stirring equipment or more Stirring object in agitation pond makes it mutually better contact with, and organic waste is fully decomposed into methane, biogas slurry and biogas residue;
Step 4: organic waste is through after fully, liquid flows into the fertile pond of water pressure chamber flow direction storage and carries out in anaerobic fermentation retort Storage fertilizer;
Step 5: the waste liquid after storage fertilizer uses the processing mode that is combined of A2O techniques and SBR techniques, through precipitation, anaerobism, it is aerobic, Precipitation, is discharged at reflux again after the processing of artificial swamp oxidation pond is up to standard.
9. a kind of domestic organic garbage processing method according to claim 8, it is characterised in that:In step 2, methane is logical It crosses desulfurizer and enters air accumulator storage, when using process of methane, biogas accesses field of employment again by fire-retarding device, to prevent Pressure inside the tank is insufficient, and flare string is back at flame-retardant device water level, automatic distinguishing kindling material.
CN201810793807.3A 2018-07-19 2018-07-19 A kind of domestic organic garbage processing system and method Pending CN108641921A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109749921A (en) * 2019-01-17 2019-05-14 浙江顺盈智能科技有限公司 Buried type integrated anaerobic fermentation terminal system
WO2020220409A1 (en) * 2019-04-30 2020-11-05 贵州民族大学 Integrated treatment system for domestic garbage
CN112517595A (en) * 2019-09-17 2021-03-19 诸暨市绿净节能环保科技有限公司 Novel intelligent organic garbage treatment system
CN112517594A (en) * 2019-09-17 2021-03-19 诸暨市绿净节能环保科技有限公司 Environment-friendly intelligent organic garbage disposal system

Citations (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201049945Y (en) * 2006-11-15 2008-04-23 高正连 Cold belt open type heating methane tank device
CN201971803U (en) * 2011-01-10 2011-09-14 安徽思嘉永志环能设备科技有限公司 Methane purifying device
CN202028606U (en) * 2011-05-03 2011-11-09 朱涛 Integrated treatment system for municipal organic garbage
CN102357506A (en) * 2011-08-01 2012-02-22 牛心红 Method for wet treatment and resource utilization of household garbage
CN202208720U (en) * 2011-08-23 2012-05-02 杨斯智 Foldable methane and biogas manure anaerobic reaction device
CN102674548A (en) * 2012-05-09 2012-09-19 广州市市政工程设计研究院 Sequencing batch A2O sewage treatment method and device
CN202465451U (en) * 2011-11-30 2012-10-03 杭州市人民政府农村能源办公室 Landfill leachate treatment system
KR101342982B1 (en) * 2012-09-05 2013-12-18 비케이환경종합건설 주식회사 A bio gas manufacturing system using livestock excretions and food waste
KR20140004989A (en) * 2012-07-04 2014-01-14 최영철 Hybrid thermophilic anaerobic digestion process for the combined treatment of food-waste and pig-manure.
CN204657081U (en) * 2014-12-29 2015-09-23 广西盛捷新业环保科技有限公司 Living standard of urban and rural population rubbish, sewage recycling ecology synthesis treating apparatus
CN105800874A (en) * 2016-05-06 2016-07-27 广西神州环保设施运营有限责任公司 Urban domestic sewage and garbage integrated and circular type centralized treatment system
CN206033742U (en) * 2016-06-22 2017-03-22 华伟 Kitchen garbage integrated processing system
CN206538413U (en) * 2017-02-08 2017-10-03 侯隆飙 Four seasons firedamp gas equipment in greenhouse
CN108217943A (en) * 2018-01-29 2018-06-29 郑州轻工业学院 S-UASB sludge anaerobics installation for fermenting couples preposition anoxic A2O denitrification dephosphorization apparatus and the method for handling sludge
CN208684944U (en) * 2018-07-19 2019-04-02 诸暨市绿净节能环保科技有限公司 A kind of domestic organic garbage processing system

Patent Citations (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201049945Y (en) * 2006-11-15 2008-04-23 高正连 Cold belt open type heating methane tank device
CN201971803U (en) * 2011-01-10 2011-09-14 安徽思嘉永志环能设备科技有限公司 Methane purifying device
CN202028606U (en) * 2011-05-03 2011-11-09 朱涛 Integrated treatment system for municipal organic garbage
CN102357506A (en) * 2011-08-01 2012-02-22 牛心红 Method for wet treatment and resource utilization of household garbage
CN202208720U (en) * 2011-08-23 2012-05-02 杨斯智 Foldable methane and biogas manure anaerobic reaction device
CN202465451U (en) * 2011-11-30 2012-10-03 杭州市人民政府农村能源办公室 Landfill leachate treatment system
CN102674548A (en) * 2012-05-09 2012-09-19 广州市市政工程设计研究院 Sequencing batch A2O sewage treatment method and device
KR20140004989A (en) * 2012-07-04 2014-01-14 최영철 Hybrid thermophilic anaerobic digestion process for the combined treatment of food-waste and pig-manure.
KR101342982B1 (en) * 2012-09-05 2013-12-18 비케이환경종합건설 주식회사 A bio gas manufacturing system using livestock excretions and food waste
CN204657081U (en) * 2014-12-29 2015-09-23 广西盛捷新业环保科技有限公司 Living standard of urban and rural population rubbish, sewage recycling ecology synthesis treating apparatus
CN105800874A (en) * 2016-05-06 2016-07-27 广西神州环保设施运营有限责任公司 Urban domestic sewage and garbage integrated and circular type centralized treatment system
CN206033742U (en) * 2016-06-22 2017-03-22 华伟 Kitchen garbage integrated processing system
CN206538413U (en) * 2017-02-08 2017-10-03 侯隆飙 Four seasons firedamp gas equipment in greenhouse
CN108217943A (en) * 2018-01-29 2018-06-29 郑州轻工业学院 S-UASB sludge anaerobics installation for fermenting couples preposition anoxic A2O denitrification dephosphorization apparatus and the method for handling sludge
CN208684944U (en) * 2018-07-19 2019-04-02 诸暨市绿净节能环保科技有限公司 A kind of domestic organic garbage processing system

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘荣厚: "全国高等农业院校教材 新能源工程", 中国农业出版社, pages: 206 *
高世江: "废水生物脱氮除磷工艺研究进展", 科技资讯, no. 4, pages 51 - 52 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109749921A (en) * 2019-01-17 2019-05-14 浙江顺盈智能科技有限公司 Buried type integrated anaerobic fermentation terminal system
WO2020220409A1 (en) * 2019-04-30 2020-11-05 贵州民族大学 Integrated treatment system for domestic garbage
CN112517595A (en) * 2019-09-17 2021-03-19 诸暨市绿净节能环保科技有限公司 Novel intelligent organic garbage treatment system
CN112517594A (en) * 2019-09-17 2021-03-19 诸暨市绿净节能环保科技有限公司 Environment-friendly intelligent organic garbage disposal system

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