CN111848258A - Rapid conversion system of biomass to gas-liquid solid fertilizer - Google Patents
Rapid conversion system of biomass to gas-liquid solid fertilizer Download PDFInfo
- Publication number
- CN111848258A CN111848258A CN202010754306.1A CN202010754306A CN111848258A CN 111848258 A CN111848258 A CN 111848258A CN 202010754306 A CN202010754306 A CN 202010754306A CN 111848258 A CN111848258 A CN 111848258A
- Authority
- CN
- China
- Prior art keywords
- biogas
- tank
- gas
- biomass
- port
- 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.)
- Pending
Links
- 239000003337 fertilizer Substances 0.000 title claims abstract description 28
- 239000007788 liquid Substances 0.000 title claims abstract description 23
- 238000006243 chemical reaction Methods 0.000 title claims abstract description 22
- 239000007787 solid Substances 0.000 title claims abstract description 20
- 239000002028 Biomass Substances 0.000 title claims abstract description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 98
- 238000000855 fermentation Methods 0.000 claims abstract description 56
- 239000002002 slurry Substances 0.000 claims abstract description 54
- 230000004151 fermentation Effects 0.000 claims abstract description 30
- 239000002994 raw material Substances 0.000 claims abstract description 5
- 238000003860 storage Methods 0.000 claims description 28
- 238000010438 heat treatment Methods 0.000 claims description 19
- 235000013311 vegetables Nutrition 0.000 claims description 13
- 239000003895 organic fertilizer Substances 0.000 claims description 9
- 238000009423 ventilation Methods 0.000 claims description 9
- 230000001276 controlling effect Effects 0.000 claims description 3
- 230000001105 regulatory effect Effects 0.000 claims description 3
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 7
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 6
- 229910052700 potassium Inorganic materials 0.000 abstract description 5
- 239000000463 material Substances 0.000 abstract description 4
- 230000005611 electricity Effects 0.000 abstract description 3
- 238000004064 recycling Methods 0.000 abstract description 3
- 239000000654 additive Substances 0.000 abstract description 2
- 230000015556 catabolic process Effects 0.000 abstract description 2
- 238000006731 degradation reaction Methods 0.000 abstract description 2
- 235000021049 nutrient content Nutrition 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 19
- 238000000034 method Methods 0.000 description 8
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 230000000694 effects Effects 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 6
- 239000002699 waste material Substances 0.000 description 6
- 238000005516 engineering process Methods 0.000 description 5
- 235000011299 Brassica oleracea var botrytis Nutrition 0.000 description 4
- 240000003259 Brassica oleracea var. botrytis Species 0.000 description 4
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 4
- 239000004202 carbamide Substances 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- 235000015097 nutrients Nutrition 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 230000005855 radiation Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 239000011358 absorbing material Substances 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 238000007792 addition Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 210000003608 fece Anatomy 0.000 description 2
- 230000005764 inhibitory process Effects 0.000 description 2
- 239000010871 livestock manure Substances 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 229920000742 Cotton Polymers 0.000 description 1
- 241000219112 Cucumis Species 0.000 description 1
- 235000015510 Cucumis melo subsp melo Nutrition 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 230000004720 fertilization Effects 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 238000003973 irrigation Methods 0.000 description 1
- 230000002262 irrigation Effects 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 239000002207 metabolite Substances 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 235000021048 nutrient requirements Nutrition 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 230000029553 photosynthesis Effects 0.000 description 1
- 238000010672 photosynthesis Methods 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000010822 slaughterhouse waste Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000010902 straw Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F9/00—Fertilisers from household or town refuse
- C05F9/04—Biological compost
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G7/00—Botany in general
- A01G7/02—Treatment of plants with carbon dioxide
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G7/00—Botany in general
- A01G7/04—Electric or magnetic or acoustic treatment of plants for promoting growth
- A01G7/045—Electric or magnetic or acoustic treatment of plants for promoting growth with electric lighting
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G9/00—Cultivation in receptacles, forcing-frames or greenhouses; Edging for beds, lawn or the like
- A01G9/18—Greenhouses for treating plants with carbon dioxide or the like
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G9/00—Cultivation in receptacles, forcing-frames or greenhouses; Edging for beds, lawn or the like
- A01G9/24—Devices or systems for heating, ventilating, regulating temperature, illuminating, or watering, in greenhouses, forcing-frames, or the like
- A01G9/243—Collecting solar energy
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G9/00—Cultivation in receptacles, forcing-frames or greenhouses; Edging for beds, lawn or the like
- A01G9/24—Devices or systems for heating, ventilating, regulating temperature, illuminating, or watering, in greenhouses, forcing-frames, or the like
- A01G9/246—Air-conditioning systems
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05C—NITROGENOUS FERTILISERS
- C05C9/00—Fertilisers containing urea or urea compounds
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D7/00—Fertilisers producing carbon dioxide
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/60—Heating or cooling during the treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/964—Constructional parts, e.g. floors, covers or doors
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/964—Constructional parts, e.g. floors, covers or doors
- C05F17/971—Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material
- C05F17/979—Constructional parts, e.g. floors, covers or doors for feeding or discharging materials to be treated; for feeding or discharging other material the other material being gaseous
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/993—Arrangements for measuring process parameters, e.g. temperature, pressure or humidity
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F9/00—Fertilisers from household or town refuse
- C05F9/02—Apparatus for the manufacture
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G5/00—Fertilisers characterised by their form
- C05G5/20—Liquid fertilisers
-
- H—ELECTRICITY
- H02—GENERATION; CONVERSION OR DISTRIBUTION OF ELECTRIC POWER
- H02J—CIRCUIT ARRANGEMENTS OR SYSTEMS FOR SUPPLYING OR DISTRIBUTING ELECTRIC POWER; SYSTEMS FOR STORING ELECTRIC ENERGY
- H02J7/00—Circuit arrangements for charging or depolarising batteries or for supplying loads from batteries
- H02J7/34—Parallel operation in networks using both storage and other DC sources, e.g. providing buffering
- H02J7/35—Parallel operation in networks using both storage and other DC sources, e.g. providing buffering with light sensitive cells
-
- 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
- H02S40/00—Components or accessories in combination with PV modules, not provided for in groups H02S10/00 - H02S30/00
- H02S40/40—Thermal components
- H02S40/44—Means to utilise heat energy, e.g. hybrid systems producing warm water and electricity at the same time
-
- 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
- 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
- Y02A40/25—Greenhouse technology, e.g. cooling systems therefor
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E10/00—Energy generation through renewable energy sources
- Y02E10/60—Thermal-PV hybrids
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/12—Technologies relating to agriculture, livestock or agroalimentary industries using renewable energies, e.g. solar water pumping
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P80/00—Climate change mitigation technologies for sector-wide applications
- Y02P80/20—Climate change mitigation technologies for sector-wide applications using renewable 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
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Biochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Biotechnology (AREA)
- Environmental Sciences (AREA)
- Botany (AREA)
- Biodiversity & Conservation Biology (AREA)
- Ecology (AREA)
- Forests & Forestry (AREA)
- Power Engineering (AREA)
- Pest Control & Pesticides (AREA)
- Manufacturing & Machinery (AREA)
- Sustainable Development (AREA)
- Sustainable Energy (AREA)
- Inorganic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
生物质向气液固肥快速转化系统,由厌氧发酵罐和沼液沼渣罐两部分构成,其中,发酵罐可满足批式、间歇式、连续式厌氧发酵要求,利用尾菜垃圾及少量富含N、P、K元素的添加物作为发酵原料,不仅促进厌氧发酵过程,而且提高料液总养分含量,发酵生成的沼气通过点亮沼气灯的方式快速转化为光能、热能以及CO2气肥,发酵罐溢流口排出的料液在沼液沼渣罐内以通热空气的方式进行好氧处理,有效加快BOD、COD的降解速率,快速转化成高腐熟度的液肥,发酵结束时可将排出的沼渣直接作为固肥使用。同时,PV/T系统将光能转化为热能及电能,为发酵罐提供充足热量以及启动控制箱、水泵所需的电量。能够实现能源资源的高效循环利用。
The rapid conversion system of biomass to gas-liquid solid fertilizer is composed of two parts: anaerobic fermentation tank and biogas slurry residue tank. Among them, the fermentation tank can meet the requirements of batch, intermittent and continuous anaerobic fermentation. A small amount of additives rich in N, P, K elements are used as fermentation raw materials, which not only promotes the anaerobic fermentation process, but also increases the total nutrient content of the feed liquid. The biogas generated by fermentation is quickly converted into light energy, heat energy and CO 2 gas fertilizer, the material liquid discharged from the overflow port of the fermentation tank is aerobic treated by hot air in the biogas slurry residue tank, which can effectively speed up the degradation rate of BOD and COD, and quickly convert it into liquid fertilizer with high decomposing degree. At the end of fermentation, the discharged biogas residue can be directly used as solid fertilizer. At the same time, the PV/T system converts light energy into heat energy and electricity, providing sufficient heat for the fermentation tank and the electricity required to start the control box and water pump. It can realize the efficient recycling of energy resources.
Description
技术领域technical field
本发明涉及沼气技术领域,具体为生物质向气液固肥快速转化技术。The invention relates to the technical field of biogas, in particular to the rapid conversion technology of biomass to gas-liquid solid fertilizer.
背景技术Background technique
蔬菜废弃物具有含水率高、营养丰富等特性。通常尾菜垃圾中的固体(干物质)含量为8%~15%,干物质中有机质占比80%~95%。Vegetable waste has the characteristics of high moisture content and rich nutrition. Usually, the solid (dry matter) content in the tail vegetable garbage is 8% to 15%, and the organic matter in the dry matter accounts for 80% to 95%.
传统处理有机废弃物的方式主要为填埋或焚烧。填埋易于操作,但通常动用大量人力物力,又占用宝贵的土地资源,投入成本越来越高。焚烧能迅速缩减废弃物体积,产生的热量可用作热能发电,但往往因为焚烧条件和手段的不当而引发大气污染问题。The traditional way of dealing with organic waste is mainly landfill or incineration. Landfilling is easy to operate, but it usually consumes a lot of manpower and material resources, occupies valuable land resources, and the input cost is getting higher and higher. Incineration can quickly reduce the volume of waste, and the heat generated can be used as thermal energy for power generation, but it often causes air pollution problems due to improper incineration conditions and methods.
厌氧发酵技术可对尾菜固体废弃物进行降解,同时能产生沼气能源,具有较大的经济效益。然而由于尾菜中含水率较高,产生大量的沼液且沼液利用率低,并且在厌氧发酵过程中容易水解酸化,产生的挥发性脂肪酸抑制了产甲烷的过程。另外,厌氧发酵技术需要稳定热源进行恒温加热,大多处理方式热量损失和投入成本较高。Anaerobic fermentation technology can degrade the solid waste of tail vegetable, and can generate biogas energy at the same time, which has great economic benefits. However, due to the high water content in tail vegetables, a large amount of biogas slurry is produced and the utilization rate of biogas slurry is low, and it is easily hydrolyzed and acidified during the anaerobic fermentation process, and the volatile fatty acids produced inhibit the process of methane production. In addition, anaerobic fermentation technology requires a stable heat source for constant temperature heating, and most of the treatment methods have high heat loss and investment costs.
温室大棚内作物生长需要施加有机肥及二氧化碳气肥,现有技术中有机肥的制备成本相对较高,有机肥在施肥后发酵不彻底,肥料成熟度低,易造成烧苗等不利影响。The growth of crops in the greenhouse requires the application of organic fertilizer and carbon dioxide gas fertilizer. In the prior art, the preparation cost of organic fertilizer is relatively high, and the fermentation of organic fertilizer is incomplete after fertilization, and the maturity of fertilizer is low, which is easy to cause adverse effects such as burning seedlings.
发明内容SUMMARY OF THE INVENTION
本发明的目的是提供一种生物质向气液固肥快速转化系统。The purpose of the present invention is to provide a rapid conversion system of biomass to gas-liquid solid fertilizer.
本发明是生物质向气液固肥快速转化系统,包括用于进行尾菜原料发酵的厌氧发酵罐1、用于产出液体有机肥的沼液沼渣罐2,用于储存热空气的大棚龙骨3,用于熟化沼液沼渣的通风管道4,用于进行光热及光电转化的PV/T板5,用于储存热水加热发酵罐的蓄热水箱6,用于加热发酵罐1的盘管14,用于收集沼气的集气袋7,用于点燃沼气的沼气灯8,用于控制水泵、风机启停的控制箱9,用于调控和保护PV/T板线路5的控制逆变一体机40,以及储存电能的蓄电池组39,所述厌氧发酵罐1包括输入口和输出口,所述厌氧发酵罐1的输入口为进料口10,所述厌氧发酵罐的输出口包括沼气输出口11、沼渣排放口12和沼液溢流口13,所述沼气输出口11连接集气袋7,所述集气袋7输出端连接沼气灯8,所述沼液溢流口13连接所述沼液沼渣罐2,所述沼液沼渣罐2包括进风口43、进料口21、排气口42及排料口18,所述PV/T板5连接蓄热水箱6,所述蓄热水箱6连接厌氧发酵罐加热盘管14,所述通风管道4输入口连接大棚龙骨3,所述通风管道4输出口连接沼液沼渣罐2。The present invention is a rapid conversion system of biomass to gas-liquid solid fertilizer, including an
与现有技术相比,本发明的有益效果是:1.系统通过厌氧发酵的方式将尾菜降解,变废为宝,实现了资源的循环利用。2.系统充分利用太阳辐射热量,通过PV/T系统不仅对温室大棚起到了遮阴的效果,而且将光能转化为热能及电能,其中转化的热能,以水为介质储存在水箱内,给发酵罐提供热量,转化的电能储存在蓄电池组中,用于启动控制箱、水泵。3.将尿素化肥与尾菜按比例放入发酵罐中,调节发酵pH及C/N,缓解酸抑制过程,促进产气,也使排出的沼液沼渣中N、P、K等养分含量大大提升。并利用风机将大棚龙骨中的热空气通入沼液沼渣罐,加快料液BOD、COD的降解速率,使沼液沼渣深度熟化,达到了快速生产液肥固肥的效果。4.厌氧发酵产生的沼气通过点亮沼气灯的方式,快速转化为二氧化碳气肥,并且给大棚增温补光,强化光合作用,促进作物生长。Compared with the prior art, the present invention has the following beneficial effects: 1. The system degrades the tail vegetable by anaerobic fermentation, turns waste into treasure, and realizes the recycling of resources. 2. The system makes full use of solar radiation heat. The PV/T system not only provides shade for the greenhouse, but also converts light energy into heat energy and electrical energy. The converted heat energy is stored in the water tank with water as the medium to provide The fermentation tank provides heat, and the converted electrical energy is stored in the battery pack for starting the control box and water pump. 3. Put the urea fertilizer and the tail vegetable into the fermentation tank in proportion to adjust the fermentation pH and C/N, ease the acid inhibition process, promote gas production, and also increase the N, P, K and other nutrients in the discharged biogas slurry and residue. Huge improvements. And the hot air in the greenhouse keel is passed into the biogas slurry and biogas residue tank by the fan to speed up the degradation rate of BOD and COD of the feed liquid, so that the biogas slurry and biogas residue is deeply matured, and the effect of rapid production of liquid fertilizer and solid fertilizer is achieved. 4. The biogas produced by anaerobic fermentation is quickly converted into carbon dioxide gas fertilizer by lighting the biogas lamp, and the greenhouse is heated and supplemented with light, which strengthens photosynthesis and promotes the growth of crops.
附图说明Description of drawings
图1是本发明的实施例的系统结构图,图2为本发明厌氧发酵罐示意图,图3为本发明沼液沼渣罐示意图。Fig. 1 is a system structure diagram of an embodiment of the present invention, Fig. 2 is a schematic diagram of an anaerobic fermentation tank of the present invention, and Fig. 3 is a schematic diagram of a biogas slurry and biogas residue tank of the present invention.
具体实施方式Detailed ways
如图1、图2所示,本发明是生物质向气液固肥快速转化系统,包括用于进行尾菜原料发酵的厌氧发酵罐1、用于产出液体有机肥的沼液沼渣罐2,用于储存热空气的大棚龙骨3,用于熟化沼液沼渣的通风管道4,用于进行光热及光电转化的PV/T板5,用于储存热水加热发酵罐的蓄热水箱6,用于加热发酵罐1的盘管14,用于收集沼气的集气袋7,用于点燃沼气的沼气灯8,用于控制水泵、风机启停的控制箱9,用于调控和保护PV/T板线路5的控制逆变一体机40,以及储存电能的蓄电池组39,所述厌氧发酵罐1包括输入口和输出口,所述厌氧发酵罐1的输入口为进料口10,所述厌氧发酵罐的输出口包括沼气输出口11、沼渣排放口12和沼液溢流口13,所述沼气输出口11连接集气袋7,所述集气袋7输出端连接沼气灯8,所述沼液溢流口13连接所述沼液沼渣罐2,所述沼液沼渣罐2包括进风口43、进料口21、排气口42及排料口18,所述PV/T板5连接蓄热水箱6,所述蓄热水箱6连接厌氧发酵罐加热盘管14,所述通风管道4输入口连接大棚龙骨3,所述通风管道4输出口连接沼液沼渣罐2。As shown in Fig. 1 and Fig. 2, the present invention is a rapid conversion system of biomass to gas-liquid solid fertilizer, including an
本发明能够解决传统尾菜厌氧发酵容易酸化,抑制厌氧产甲烷的过程的问题,在厌氧发酵罐中添加尿素等外源添加物,既能促进产气,同时也大大提升了沼液沼渣的养分。并且,有效利用了太阳辐射热能,通过PV/T系统光热及光电转换原理,为发酵罐提供充足热量以及启动控制箱、水泵所需的电量。本系统不仅实现了尾菜资源高效循环利用,而且高效利用能源,将尾菜垃圾快速转化为气液固肥,促进温室大棚作物高质量生长。The method can solve the problem that the traditional anaerobic fermentation of tail vegetables is easy to acidify and inhibit the process of anaerobic methane production, and the addition of exogenous additives such as urea in the anaerobic fermentation tank can not only promote gas production, but also greatly improve the biogas slurry. The nutrients of the digestate. In addition, the solar radiation heat energy is effectively utilized, and through the photothermal and photoelectric conversion principle of the PV/T system, sufficient heat is provided for the fermentation tank and the electricity required to start the control box and the water pump is provided. The system not only realizes the efficient recycling of cauliflower resources, but also efficiently utilizes energy, quickly converts cauliflower waste into gas-liquid solid fertilizer, and promotes high-quality growth of greenhouse crops.
如图1所示,厌氧发酵罐1罐外设有加热盘管14及温度传感器15,所述温度传感器15连接控制箱9。其中,厌氧发酵罐1容积为 0.56m3。As shown in FIG. 1 , a
如图1、图2所示,所述发酵罐进料口10为有倾斜角度的漏斗形状,竖直方向偏离15°,并且发酵原料为尾菜垃圾及少量尿素等富含N、P、K元素的外源添加物。As shown in Figure 1 and Figure 2, the
如图1、图2所示,所述沼气输出口11后连接气体阀门41,所述气体阀门41后连接集气袋7。As shown in FIG. 1 and FIG. 2 , a
如图1所示,所述集气袋7输出口连接阀门16,所述阀门16连接沼气增压泵17,所述沼气增压泵17连接沼气灯8。As shown in FIG. 1 , the output port of the gas collection bag 7 is connected to a
如图1、图2、图3所示,所述沼液溢流口13输出端连接沼液沼渣罐输入口21。As shown in FIG. 1 , FIG. 2 and FIG. 3 , the output end of the biogas
如图1所示,所述沼液沼渣罐2内设有温度传感器22。其中,沼液沼渣罐2容积为0.27m3。As shown in FIG. 1 , a temperature sensor 22 is provided in the
如图1所示,所述大棚龙骨3为空心管道,所述大棚龙骨3空心管道输出口连接阀门23,所述阀门23连接风机24,所述风机24出风口连接沼液沼渣罐进风口管道25。As shown in Figure 1, the
如图1所示,所述蓄热水箱6设有进出水口,所述蓄热水箱一端出水口26连接阀门27,所述阀门27连接水泵28,所述水泵28连接PV/T板进水口29,所述蓄热水箱一端进水口30连接PV/T板出水口31。所述蓄热水箱一端出水口32连接阀门33,所述阀门33连接水泵34,所述水泵34连接发酵罐盘管进水口35,所述蓄热水箱一端进水口36连接发酵罐盘管出水口37。As shown in FIG. 1 , the hot
如图1所示,所述蓄热水箱6设有温度传感器38,所述温度传感器38连接控制箱9。As shown in FIG. 1 , the hot
如图1所示,所述PV/T板5连接控制逆变一体机40,所述控制逆变一体机40分别连接控制箱9及蓄电池组39。As shown in FIG. 1 , the PV/
为了使本发明的目的、技术方案及优点更加清楚明白,以下结合附图及实施例,对本发明进行进一步详细说明。应当理解,此处所描述的具体实施例仅用以解释本发明,并不用于限定本发明。需要说明的是,如果不冲突,本发明实施例中的各个特征可以相互结合,均在本发明的保护范围之内。In order to make the objectives, technical solutions and advantages of the present invention clearer, the present invention will be further described in detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are only used to explain the present invention, but not to limit the present invention. It should be noted that, if there is no conflict, various features in the embodiments of the present invention can be combined with each other, which are all within the protection scope of the present invention.
本发明中提及到的有机肥俗称农家肥,包括以各种动物、植物残体或代谢物成,如人畜粪便、秸秆、动物残体、屠宰场废弃物等。有机肥是采用物理、化学、生物或三者兼有的处理技术,经过一定的加工工艺,达到无害化标准而形成的,符合国家相关标准及法规的一类肥料。本发明提到的有机肥养分要求主要遵循《有机-无机复混液体肥料》标准,其中,有机质≥150 g/L,总养分≥110 g/L。The organic fertilizer mentioned in the present invention is commonly known as farmyard manure, including various animal and plant residues or metabolites, such as human and animal manure, straw, animal residues, slaughterhouse waste and the like. Organic fertilizer is a kind of fertilizer that is formed by using physical, chemical, biological or all three treatment technologies, through certain processing technology, to achieve harmless standards, and in line with relevant national standards and regulations. The nutrient requirements of the organic fertilizer mentioned in the present invention mainly follow the standard of "Organic-Inorganic Compound Liquid Fertilizer", wherein the organic matter is greater than or equal to 150 g/L, and the total nutrients are greater than or equal to 110 g/L.
本发明中提到的沼液好氧处理要求主要遵循《农田灌溉水质标准》,其中,加工、烹饪及去皮蔬菜化学需氧量≤100 mg/L、生食类蔬菜、瓜类和草本水果化学需氧量≤60 mg/L、凯氏氮≤30 mg/L、总磷≤10 mg/L、水温≤35℃、pH在5.8~8.5。The requirements for aerobic treatment of biogas slurry mentioned in the present invention mainly follow the "Water Quality Standard for Farmland Irrigation", wherein the chemical oxygen demand of processed, cooked and peeled vegetables is ≤100 mg/L, raw vegetables, melons and herbal fruits are chemically Oxygen demand ≤ 60 mg/L, Kjeldahl nitrogen ≤ 30 mg/L, total phosphorus ≤ 10 mg/L, water temperature ≤ 35 ℃, pH 5.8~8.5.
在本实施例中,厌氧发酵罐1罐内设有加热盘管14,用于加热发酵罐,内置温度传感器(15),控制罐内温度恒定。其中,加热盘管盘在发酵罐侧壁,有利于罐体均匀受热。温度传感器15至于发酵罐侧壁中部,测得的温度误差较小。温度传感器15将测量的温度信号反馈给控制箱9,再由控制箱9控制水泵启停,实现发酵罐的恒温加热效果。发酵罐(1)罐内温度应保持在37±1℃。如图2所示,厌氧发酵罐1长1m,宽0.7m,高0.8m,容积为 0.56m3,能够消纳一般温室产生的尾菜垃圾,且发酵罐1有效容积一般为罐体容积的 80% ~ 85%。In this embodiment, a
在本实施例中,发酵罐进料口10加入尾菜及尿素等富含N、P、K元素的物质,可调节料液pH及C/N,缓解酸抑制过程,促进产气,也使排出的沼液沼渣中的总氮、总磷、总钾等养分大大提高。另外,发酵罐进料口10为有倾斜角度的漏斗形状,竖直方向偏离15°,使物料滑入罐中,方便进料。In the present embodiment, the
在本实施例中,沼气输出口11后连接气体阀门12,气体阀门12后连接集气袋7,集气袋7输出口连接阀门16,阀门16连接沼气增压泵17,沼气增压泵17连接沼气灯8。其中,沼气增压泵可增加沼气压力,使沼气灯易于点燃。In this embodiment, the
在本实施例中,沼液溢流口13输出端连接沼液沼渣罐输入口21,在连续式及间歇式发酵模式下,进料时,水位达到溢流口位置时,沼液将自动排入沼液沼渣罐2,可满足连续/间歇进出料要求。In this embodiment, the output end of the biogas
在本实施例中,如图3所示,沼液沼渣罐2长0.6m,宽0.6m,高0.75m,容积为0.27m3,能够处理从发酵罐1中溢流出的沼液。沼液沼渣罐2内设有温度传感器22,温度传感器22连接控制箱9。其中,温度传感器22至于罐侧壁中部,测得的温度误差较小。温度传感器22将测量的温度信号反馈给控制箱9,再由控制箱9控制风机启停,实现对沼液沼渣罐2中料液的温度控制。沼液沼渣罐2体上侧设有排气口42,用于排放空气以及反应产生的氮气、氨气。另外,好氧处理所需热量由沼液余热及热空气提供,能够满足好氧温度要求。In this embodiment, as shown in FIG. 3 , the biogas
在本实施例中,大棚龙骨3为空心管道,表面涂有吸热材料,大棚龙骨3空心管道输出口连接阀门23,阀门23连接风机24,风机24出风口连接沼液沼渣罐进风口管道25。其中,龙骨3将太阳辐射热量及PV/T板5背面热量吸收加热龙骨内空气,龙骨表面涂吸热材料加强换热效果。In this embodiment, the
在本实施例中,蓄热水箱6设有进出水口,蓄热水箱一端出水口26连接阀门27,阀门27连接水泵28,水泵28连接PV/T板进水口29,蓄热水箱一端进水口30连接PV/T板出水口31。利用PV/T板的光热转化原理,通过水泵将蓄热水箱中的水进行循环加热。蓄热水箱一端出水口32连接阀门33,阀门33连接水泵34,水泵34连接发酵罐盘管进水口35,蓄热水箱一端进水口36连接发酵罐盘管出水口37。通过水泵将蓄热水箱中的水抽到加热盘管进水口加热发酵罐,再由盘管出水口流入水箱形成循环。In this embodiment, the hot
在本实施例中,所述蓄热水箱6设有温度传感器38,所述温度传感器38连接控制箱9。温度传感器38至于水箱侧壁中部,测得的温度误差较小。温度传感器38将测量的温度信号反馈给控制箱9,再由控制箱9控制低速运转水泵的启停,提升水箱热水的升温效果。In this embodiment, the hot
另外,发酵罐1、蓄热水箱6、沼液沼渣罐2外侧均包裹保温棉,减少热量散失。In addition, the outside of the
以上所述,只是本发明的较佳实施例而已,本发明并不局限于上述实施方式,只要其以相同的手段达到本发明的技术效果,都应属于本发明的保护范围。The above descriptions are only preferred embodiments of the present invention, and the present invention is not limited to the above-mentioned embodiments, as long as the technical effects of the present invention are achieved by the same means, they should all belong to the protection scope of the present invention.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010754306.1A CN111848258A (en) | 2020-07-31 | 2020-07-31 | Rapid conversion system of biomass to gas-liquid solid fertilizer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010754306.1A CN111848258A (en) | 2020-07-31 | 2020-07-31 | Rapid conversion system of biomass to gas-liquid solid fertilizer |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN111848258A true CN111848258A (en) | 2020-10-30 |
Family
ID=72945259
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010754306.1A Pending CN111848258A (en) | 2020-07-31 | 2020-07-31 | Rapid conversion system of biomass to gas-liquid solid fertilizer |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN111848258A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114686406A (en) * | 2022-05-13 | 2022-07-01 | 兰州理工大学 | Solar PVT (physical vapor pressure temperature) controlled anaerobic and aerobic fermentation agricultural and animal waste rapid treatment method |
| CN114891604A (en) * | 2022-05-24 | 2022-08-12 | 兰州理工大学 | Backheating quality recovery system applied to large-scale treatment of waste vegetables |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN204490868U (en) * | 2015-02-09 | 2015-07-22 | 淄博淄川金毫相富硒农产品专业合作社 | Biomass energy bionethanation system |
| CN205115313U (en) * | 2015-10-26 | 2016-03-30 | 厦门市联谊吉源环保工程有限公司 | Quick curing treatment facility of anaerobism natural pond sediment |
| CN107511388A (en) * | 2017-07-24 | 2017-12-26 | 深圳市海吉星环保有限责任公司 | A kind of organic perishable garbage anaerobic fermentation cogeneration of heat and power biogas slurry fertilizer manufacture and system |
| CN107815409A (en) * | 2017-11-10 | 2018-03-20 | 陈建峰 | A kind of solar assisted methane fermentation device |
| CN207760331U (en) * | 2017-11-22 | 2018-08-24 | 甘肃省科学院自然能源研究所 | A kind of domestic solar biogas fermentation device of processing vegetables waste dish |
| CN108998356A (en) * | 2018-09-28 | 2018-12-14 | 淮安市农业环境保护监测站 | The biogas recirculation utilizing works system of waste dish step fermentation |
| CN109206172A (en) * | 2018-09-26 | 2019-01-15 | 上海市政工程设计研究总院(集团)有限公司 | A kind of organic waste anaerobic fermentation biogas residue fertilizer producing system and method |
| CN110272923A (en) * | 2019-06-27 | 2019-09-24 | 南京万德斯环保科技股份有限公司 | Method and system for resource utilization of coriander waste |
-
2020
- 2020-07-31 CN CN202010754306.1A patent/CN111848258A/en active Pending
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN204490868U (en) * | 2015-02-09 | 2015-07-22 | 淄博淄川金毫相富硒农产品专业合作社 | Biomass energy bionethanation system |
| CN205115313U (en) * | 2015-10-26 | 2016-03-30 | 厦门市联谊吉源环保工程有限公司 | Quick curing treatment facility of anaerobism natural pond sediment |
| CN107511388A (en) * | 2017-07-24 | 2017-12-26 | 深圳市海吉星环保有限责任公司 | A kind of organic perishable garbage anaerobic fermentation cogeneration of heat and power biogas slurry fertilizer manufacture and system |
| CN107815409A (en) * | 2017-11-10 | 2018-03-20 | 陈建峰 | A kind of solar assisted methane fermentation device |
| CN207760331U (en) * | 2017-11-22 | 2018-08-24 | 甘肃省科学院自然能源研究所 | A kind of domestic solar biogas fermentation device of processing vegetables waste dish |
| CN109206172A (en) * | 2018-09-26 | 2019-01-15 | 上海市政工程设计研究总院(集团)有限公司 | A kind of organic waste anaerobic fermentation biogas residue fertilizer producing system and method |
| CN108998356A (en) * | 2018-09-28 | 2018-12-14 | 淮安市农业环境保护监测站 | The biogas recirculation utilizing works system of waste dish step fermentation |
| CN110272923A (en) * | 2019-06-27 | 2019-09-24 | 南京万德斯环保科技股份有限公司 | Method and system for resource utilization of coriander waste |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114686406A (en) * | 2022-05-13 | 2022-07-01 | 兰州理工大学 | Solar PVT (physical vapor pressure temperature) controlled anaerobic and aerobic fermentation agricultural and animal waste rapid treatment method |
| CN114891604A (en) * | 2022-05-24 | 2022-08-12 | 兰州理工大学 | Backheating quality recovery system applied to large-scale treatment of waste vegetables |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101914572B (en) | Method for Energy Utilization of Carbon Dioxide Zero Emission Type Organic Waste | |
| Wang et al. | Effect of addition of biogas slurry for anaerobic fermentation of deer manure on biogas production | |
| CN101920258B (en) | Energy utilization system of organic wastes with zero emission of carbon dioxide | |
| CN102500604B (en) | Household solid garbage recycling and renewable biological carbon circulating technology | |
| CN101225003A (en) | Farm crop straw anaerobic fermentation treatment method | |
| CN204509147U (en) | A kind of device of agricultural wastes high temperature quick fermentation production fertilizer | |
| CN107574115A (en) | A kind of industrial bio matter biogas project application system | |
| CN204630092U (en) | A kind of energy-conservation anaerobic reaction device | |
| CN101503313B (en) | Stalk air fertilizer coproduction method and matching apparatus thereof | |
| CN201865755U (en) | Biogas power generation system | |
| CN109678574A (en) | The fermentation of stalk waste takes thermal and application method | |
| CN111848258A (en) | Rapid conversion system of biomass to gas-liquid solid fertilizer | |
| US20170354086A1 (en) | System and method for anaerobic digestion of animal wastes | |
| CN208121090U (en) | A kind of industrial bio matter biogas project application system | |
| CN208995404U (en) | A kind of equipment that agricultural wastes recycle production organic fertilizer | |
| CN114686406A (en) | Solar PVT (physical vapor pressure temperature) controlled anaerobic and aerobic fermentation agricultural and animal waste rapid treatment method | |
| CN106007285A (en) | Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method | |
| CN110526533A (en) | The method of scale livestock farming comprehensive utilization of waste | |
| CN201686689U (en) | The device used in the method for preparing biomass straw biogas | |
| CN212833539U (en) | A rapid conversion system of biomass to gas-liquid solid fertilizer | |
| CN209652190U (en) | The fermentation of stalk waste takes thermal | |
| CN108570483A (en) | A method of it improving stalk fermentation and prepares biogas | |
| CN207581801U (en) | A kind of mixed material fermentation and biogas production device with low temperature sterilization | |
| CN102643693A (en) | Process for producing biogas by utilizing methane-straw gas coproduction device | |
| CN106631196A (en) | Light movable vegetable waste anaerobic dry fermentation system and method for anaerobic fermentation by using light movable vegetable waste anaerobic dry fermentation system |
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 | ||
| WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20201030 |
|
| WD01 | Invention patent application deemed withdrawn after publication |