CN108636992A - garden waste processing system - Google Patents
garden waste processing system Download PDFInfo
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- CN108636992A CN108636992A CN201810588649.8A CN201810588649A CN108636992A CN 108636992 A CN108636992 A CN 108636992A CN 201810588649 A CN201810588649 A CN 201810588649A CN 108636992 A CN108636992 A CN 108636992A
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- Prior art keywords
- fermentation
- garden waste
- discarded
- waste processing
- processing system
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- 239000010921 garden waste Substances 0.000 title claims abstract description 71
- 238000000855 fermentation Methods 0.000 claims abstract description 133
- 230000004151 fermentation Effects 0.000 claims abstract description 133
- 239000000203 mixture Substances 0.000 claims abstract description 50
- 239000008187 granular material Substances 0.000 claims abstract description 27
- 239000000463 material Substances 0.000 claims abstract description 20
- 239000011265 semifinished product Substances 0.000 claims abstract description 19
- 239000002068 microbial inoculum Substances 0.000 claims abstract description 16
- 238000003763 carbonization Methods 0.000 claims description 34
- 239000003610 charcoal Substances 0.000 claims description 14
- 239000002699 waste material Substances 0.000 claims description 14
- 239000004744 fabric Substances 0.000 claims description 13
- 238000007599 discharging Methods 0.000 claims description 11
- 239000000047 product Substances 0.000 claims description 7
- 239000002023 wood Substances 0.000 claims description 6
- 239000006227 byproduct Substances 0.000 claims description 5
- 239000002689 soil Substances 0.000 claims description 5
- 235000021419 vinegar Nutrition 0.000 claims description 5
- 239000000052 vinegar Substances 0.000 claims description 5
- 238000003756 stirring Methods 0.000 claims description 4
- 239000011276 wood tar Substances 0.000 claims description 4
- 238000005273 aeration Methods 0.000 claims 2
- 244000005700 microbiome Species 0.000 abstract description 12
- 238000005516 engineering process Methods 0.000 abstract description 3
- 238000004904 shortening Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 13
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 8
- 229910052799 carbon Inorganic materials 0.000 description 8
- 238000002156 mixing Methods 0.000 description 7
- 239000003516 soil conditioner Substances 0.000 description 5
- 230000008901 benefit Effects 0.000 description 4
- 235000021050 feed intake Nutrition 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 238000000034 method Methods 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 210000003608 fece Anatomy 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- 244000025254 Cannabis sativa Species 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 241000287828 Gallus gallus Species 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 230000009919 sequestration Effects 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
-
- 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
- C05F17/50—Treatments combining two or more different biological or biochemical treatments, e.g. anaerobic and aerobic treatment or vermicomposting and aerobic treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/80—Soil conditioners
-
- 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)
- Molecular Biology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Inorganic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Soil Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
The present invention relates to garden waste processing technology field more particularly to a kind of garden waste processing systems.The garden waste processing system of the present invention, including：Crushing system, crushing system are used to pending garden waste being ground into discarded composition granule；Hybrid system, hybrid system is used to receive a part for discarded composition granule, and itself and microbial inoculum, fermentation auxiliary material are mixed into discarded mixture；And fermentation system, fermentation system include one section of fermentation system and two sections of fermentation systems；Wherein, one section of fermentation system is fermentation semi-finished product for receiving discarded mixture, and by discarded mixture hot fermentation, and it is garden waste tunning that two sections of fermentation systems continue fermentation to fermentation semi-finished product.The garden waste processing system of the present invention, can be such that microorganism quickly breeds, and then reach shortening fermentation time during the fermentation, reduce the place that processing garden waste occupies.
Description
Technical field
The present invention relates to garden waste processing technology field more particularly to a kind of garden waste processing systems.
Background technology
In recent years, with the rapid development of urban landscaping cause, afforestation waste generates quantity and rises violently year by year.
Wherein, afforestation waste refer to urban afforestation beautification and production of forestry work in, generated limb, rhizome, fallen leaves,
Grass cuttings, flower loses and other organic wastes.
The processing modes such as stacking on the spot, landfill burning that currently processed afforestation waste mainly uses, do not only take up
Valuable land resource, and most wastes are all not carried out recycling, therefore, are built to urban ecological environment
If bringing certain influence.
Since afforestation waste constituent is mainly organic matter, it is important biomass resource.Therefore, Ke Yitong
Development biological organic fertilizer is crossed, so that it is obtained effective recycling, and considerable warp can be created by industrialized development
Benefit of helping and social benefit, meanwhile, the objective requirement for also complying with Developing Circulation Economy in Cities, making low carbon city.
But the whole process that garden waste is degraded is needed 30-40 days time by microorganism, degradation process is slow
Slowly, so still needing to be fermented with a large amount of place stacking garden waste.
Therefore, for the above deficiency, it is desirable to provide a kind of garden that garden waste can be made fast and efficiently to ferment
Woods castoff processing system.
Invention content
(1) technical problems to be solved
The technical problem to be solved by the present invention is to the time length for solving in the prior art to ferment to garden waste, places
The problem of reason garden waste needs to occupy a large amount of place.
(2) technical solution
In order to solve the above technical problem, the present invention provides a kind of garden waste processing systems, including：
Crushing system, crushing system are used to pending garden waste being ground into discarded composition granule；
Hybrid system, hybrid system is used to receive a part for discarded composition granule, and it is mixed with microbial inoculum, fermentation auxiliary material
At discarded mixture；And
Fermentation system, fermentation system include one section of fermentation system and two sections of fermentation systems；Wherein,
One section of fermentation system is fermentation semi-finished product for receiving discarded mixture, and by discarded mixture hot fermentation, two
It is garden waste tunning that section fermentation system continues fermentation to fermentation semi-finished product.
Further, crushing system includes：
Pending garden waste is cut into sheet waste by level-one crushing system, level-one crushing system；With
Sheet waste is crushed the discarded composition granule for predefined size by two level crushing system, two level crushing system.
Further, garden waste processing system further includes：
Carbonization system, carbonization system are used to receive another part of discarded composition granule, and it is garden waste to be carbonized
Charcoal；Wherein, garden waste charcoal is used to be mixed into soil conditioner with garden waste tunning.
Further, garden waste processing system further includes：
Discharging bin, discharging bin include a feeding mouth and two discharge ports；Wherein, the outlet of feeding mouth and crushing system connects
It connects, one in discharge port connect with the entrance of hybrid system, another in discharge port is connect with the entrance of carbonization system.
Further, carbonization system further includes：
The outlet of exhaust gas channel, exhaust gas channel is connect with the entrance of one section of fermentation system, and height is provided for one section of fermentation system
Warm gas；With
Collection system, collection system are used to collect the carbonization by-product wood vinegar and wood tar of carbonization system generation.
Further, one section of fermentation system includes：
Fermentation roller after discarded mixture enters fermentation roller, carries out hot fermentation in fermentation roller.
Further, two sections of fermentation systems include：
Multiple distributing troughs, fermentation semi-finished product ferment in distributing trough；
Cloth system, cloth system are allocated in for the semi-finished product that will ferment in multiple distributing troughs.
Further, cloth trench bottom is equipped with aerated conduit, and aerated conduit is used for into distributing trough by fermentation semi-finished product heap
The fermentate heap body of product provides air.
Further, two sections of fermentation systems further include：
Turner, turner are used to stir the fermentate heap body in distributing trough.
Further, two sections of fermentation systems further include：
Rail relayer is migrated, rail relayer carrying turner is migrated, for driving turner to be moved between different distributing troughs.
(3) advantageous effect
The above-mentioned technical proposal of the present invention has the following advantages that compared with prior art：
The garden waste processing system of the present invention uses one section of fermentation system and carries out high temperature to discarded mixture first
Fermentation, becomes fermentation semi-finished product, is then fermented again to fermentation semi-finished product by two sections of fermentation systems, becomes garden
Woods waste tunning.The microorganism in fermenting mixture is swashed due to during the fermentation, using one section of fermentation system
It is living, and microorganism is made quickly to breed, therefore, it is possible to make fermentation process shorten to 15-25 days, make fermentation time relative to tradition
Garden waste fermentation time reduction 50%, to make processing garden waste occupy place reduce 50%.
Description of the drawings
Fig. 1 is the structural schematic diagram of garden waste processing system of the embodiment of the present invention；
Fig. 2 is the structural schematic diagram of two sections of fermentation systems in garden waste processing system of the embodiment of the present invention.
Specific implementation mode
In order to make the object, technical scheme and advantages of the embodiment of the invention clearer, below in conjunction with the embodiment of the present invention
In attached drawing, technical scheme in the embodiment of the invention is clearly and completely described, it is clear that described embodiment is
A part of the embodiment of the present invention, instead of all the embodiments.Based on the embodiments of the present invention, ordinary skill people
The every other embodiment that member is obtained without making creative work, shall fall within the protection scope of the present invention.
A kind of garden waste processing system of the embodiment of the present invention includes mainly crushing system, hybrid system and fermentation
System.Wherein, crushing system is used to pending garden waste being ground into discarded composition granule, and hybrid system is useless for receiving
A part for aerated particle object, and itself and microbial inoculum, fermentation auxiliary material are mixed into discarded mixture, fermentation system by discarded for mixing
Object fermentation is garden waste tunning.
Specifically, fermentation system includes one section of fermentation system and two sections of fermentation systems, and one section of fermentation system is useless for receiving
Mixture is abandoned, and is fermentation semi-finished product by discarded mixture hot fermentation, two sections of fermentation systems continue to ferment to fermentation semi-finished product
For garden waste tunning.
The embodiment of the present invention can be such that microorganism quickly activates due to increasing one section of fermentation system in fermentation system
And quickly breed, fermentation time is substantially reduced, so that fermentation process is shorten to 15-25 days, i.e., fermentation time is relative to traditional
The fermentation time reduction 50% of garden waste, and then the occupancy for stacking place is reduced, so that processing garden waste is occupied
Reduce 50% in place.
As shown in Figure 1, a kind of garden waste processing system of the embodiment of the present invention, includes mainly crushing system 11, mixed
Collaboration is united and fermentation system.
In embodiments of the present invention, crushing system 11 includes level-one crushing system and two level crushing system, and level-one crushes system
The outlet of system passes through the first pneumatic conveyer pipeline with the entrance of two level crushing system.Wherein, level-one crushing system will be pending
Garden waste be cut into sheet waste, two level crushing system is entered by the first Pneumatic conveying pipeline, two level crushes system
Sheet waste is crushed the discarded composition granule for predefined size by system, and discarded composition granule is sent by the second Pneumatic conveying pipeline 12
In discharging bin 13.
Since granularity is thinner, contacted with microorganism it is more abundant, therefore, in embodiments of the present invention, in order to improve microorganism
The predefined size of decomposition rate, discarded composition granule could be provided as 5-10mm.
In embodiments of the present invention, hybrid system is used to receive the part of discarded composition granule, and by itself and microbial inoculum, fermentation
Auxiliary material is mixed into discarded mixture.Wherein, microbial inoculum is high-temperature aerobic microbial inoculum.
Specifically, hybrid system includes feed intake storehouse 21, microbial inoculum storehouse 22, auxiliary material storehouse 23, mixing machine 25 and the second Belt Conveying
Machine 24.The discarded composition granule that hybrid system receives, which is contained in, to feed intake in storehouse 21, and microbial inoculum (i.e. microorganism) is contained in microbial inoculum storehouse 22,
Fermentation auxiliary material is contained in auxiliary material storehouse 23, and mixing machine is used to mix discarded composition granule, microbial inoculum, fermentation auxiliary material.Feed intake storehouse
21 outlet, the outlet in microbial inoculum storehouse 22 and the outlet in auxiliary material storehouse 23 respectively on the second belt conveyor 24, the second Belt Conveying
Machine 24 is connect with the entrance of mixing machine.Wherein, storehouse 21, microbial inoculum storehouse 22 and auxiliary material storehouse 23 while discharging are fed intake to the second Belt Conveying
On machine 24, above-mentioned material is delivered in mixing machine by the second belt conveyor 24 to be mixed, make the C/N ratios of material, moisture content,
PH value is suitble to ferment, and becomes discarded mixture.
In embodiments of the present invention, garden waste processing system further includes carbonization system 32, and carbonization system 32 is for connecing
Receive the another part for discarding composition granule, carry out low temperature pyrolyzer reaction, and be carbonized as garden waste charcoal, finally via
The cold charcoal machine 34 of carbon is discharged.Wherein, gardens charcoal is biological carbon dust.After biological carbon dust is applied in soil, it is equivalent to a carbon sequestration
Into soil, and charcoal is rich in micropore, can effectively preserve moisture and nutrient, increase soil fertility, be good soil
The ingredient of conditioner.Therefore, gardens charcoal can be used for being mixed into soil conditioner with garden waste tunning, and
Final product is made, to improve product quality.
In embodiments of the present invention, due to the raw material of carbonization system 32 also garden waste, the embodiment of the present invention
Without additionally supplying raw material to carbonization system 32, the utilization rate of garden waste is improved.
In order to make discarded composition granule made of crushing system 11 fast, easily be delivered to hybrid system and carbon respectively
Change system 32.In embodiments of the present invention, garden waste processing system further includes discharging bin 13, and discharging bin 13 enters including one
Material mouth and two discharge ports.Wherein, feeding mouth is connect by the second Pneumatic conveying pipeline 12 with the outlet of crushing system 11, is used for
It receives and discards composition granule.One in discharge port is connect by the first belt conveyor 14 with the entrance of hybrid system, and being used for will
Discarded composition granule is delivered to the storehouse 21 that feeds intake of hybrid system.Another in discharge port passes through conveying auger 31 and carbonization system 32
Entrance connection, for the discarded composition granule to be delivered to carbonization system 32.
After waste particle is carbonized, biological powdered carbon can be not only generated, can also generate high-temperature tail gas, and wood coke
The by-products such as oil, wood vinegar, in embodiments of the present invention, carbonization system 32 further include exhaust gas channel 35 and collection system 33.
The outlet of exhaust gas channel 35 is connect with the entrance of one section of fermentation system, is recycled to the high-temperature tail gas of discharge,
High temperature hot gas is provided for one section of fermentation system, to carry out heat temperature raising to fermenting mixture, it is made to carry out hot fermentation.Cause
This, one section of fermentation system to the heating energy sources of fermenting mixture in carbonization system 32, and raw material of carbonization system 32
It is garden waste, therefore, the embodiment of the present invention improves garden waste without additionally supplying raw material to carbonization system 32
Utilization rate.
Collection system 33 is used to collect the carbonization by-product of the generation of carbonization system 32, and carbonization by-product is processed into
Other products equally have economic value.
In embodiments of the present invention, one section of fermentation system includes fermentation roller 42, and discarded mixture enters fermentation roller 42
Afterwards, hot fermentation is carried out in fermentation roller 42.Specifically, the outlet of hybrid system passes through third belt conveyor 41 and fermentation
The entrance of roller 42 connects, and exhaust gas channel 35 is connected to the air inlet of fermentation roller 42, and fermenting mixture is enable to enter fermentation
In roller 42, the high-temperature tail gas generated using carbonization system 32 is fermented, and so that high-temperature aerobic microbial inoculum is quickly bred, is killed simultaneously
Harmful levels of pathogens, and vegetable seeds is inactivated.
In embodiments of the present invention, as shown in Fig. 2, two sections of fermentation systems include multiple distributing troughs and cloth system 51.Cloth
Material system 51 is connect by the 4th belt conveyor 43 with the outlet of one section of fermentation system, cloth system 51 can will fermentation half at
Product are allocated in multiple distributing troughs, so that fermentation semi-finished product is evenly distributed in distributing trough respectively, and ferment in distributing trough.
Specifically, distributing trough can be illustrated in figure 2 two.
In embodiments of the present invention, cloth trench bottom is equipped with aerated conduit 52, and the entrance of aerated conduit 52 is equipped with height
Pressure fan 53, in composting fermentation process, high pressure positive blower 53 can by aerated conduit 52 into distributing trough by fermentation semi-finished product
The fermentate heap body being piled into squeezes into air, and air is made to squeeze into inside fermentate heap body, avoids because of anoxic anaerobic reaction being added
Play causes the nutrient loss such as ammonia nitrogen.
In embodiments of the present invention, two sections of fermentation systems further include turner 54, and turner 54 is for stirring in distributing trough
Fermentate heap body, make fermentate heap body during the fermentation, it is lateral by the one of distributing trough pan feeding by stirring for turner 54
(right side is stirred to the left as shown in Figure 2) is stirred in the side of discharging, when fermentate heap temperature persistently increases, to fermentation
Object heap body carries out turning, reduces the temperature of heap body, while the heat that fermentation process generates takes away moisture.
In embodiments of the present invention, two sections of fermentation systems further include migrating rail relayer 55, migrate the carrying of rail relayer 55 and turn over throwing
Machine 54, for driving turner 54 to be moved between different distributing troughs.Meanwhile it migrating rail relayer 55 and being also equipped with self-emptying
The garden waste tunning that two sections of fermentations are completed is transported on the 5th belt conveyor 56 and exports gardens and discarded by function
Object processing system is mixed with gardens charcoal with waiting for, produces the soil conditioner of high-quality.
The concrete processing procedure of the garden waste processing system of the embodiment of the present invention is：
First, garden waste (including fruit tree branch, fallen leaves, weeds etc.), which is put into, is crushed to 5-10mm in pulverizer
The discarded composition granule of size.
Then, discarded composition granule is sent into discharging bin 13, by a part for discarded composition granule by being sent into hybrid system
Feed intake storehouse 21, is mixed in the storehouse 21 that feeds intake, microbial inoculum storehouse 22 and auxiliary material storehouse 23 while discharging to mixing machine, and fermentation mixing is obtained
Object, and it is conveyed into fermentation roller 42.Meanwhile the host of another part feeding carbonization system of composition granule is discarded, in carbonization process
The high-temperature tail gas of generation is passed through one section of fermentation system and heats up to material, and the charcoal of generation is by going out cold 34 row of charcoal machine of charcoal
Go out, the wood tar and wood vinegar of generation are collected by collection system 33.
Then, fermenting mixture carries out fermentation at elevated temperatures in fermentation roller 42 by the high-temperature tail gas of carbonization system 32.About
The semi-finished product that ferment after fermentation, are sent into the cloth system 51 of two sections of fermentation systems by one section of 5-8 hours, uniformly by material point
Cloth continues to ferment, and the garden waste tunning that two sections of fermentations are completed is defeated in two distributing troughs to fermentation semi-finished product
Go out.
Finally, garden waste tunning is mixed with the biological powdered carbon that carbonization system 32 generates, produces height
The soil conditioner of quality.
In conclusion the garden waste processing system of the embodiment of the present invention, pending garden waste is by crushing
Afterwards, the discarded composition granule of a part can enter carbonization system progress carbonization treatment (decomposition of difficulty containing microorganism tree root, plastics sundries
Deng), the wood tar generated after carbonization treatment can be separated and collected for selling, and high-temperature tail gas can provide for one section of fermentation system
Thermal energy, wood vinegar can also be mixed into discarded composition granule in addition to that can produce other products with auxiliary material (cow dung, chicken manure etc.), microbial inoculum
One section of hot fermentation of middle progress and two sections of compost fermentations.During the fermentation, equipment can provide suitable oxygen for microorganism
And moisture, garden waste tunning after fermentation can also be mixed with the charcoal in carbonisation, finally
Product is high-quality soil conditioner.The garden waste processing system of the embodiment of the present invention, not only microorganism offer are suitble to
The water content of existence, pH value environment, also heat up to material in earlier fermentation, microorganism are made quickly to breed, and then reach contracting
Short fermentation time reduces the place that processing garden waste occupies.
Finally it should be noted that：The above embodiments are merely illustrative of the technical solutions of the present invention, rather than its limitations；Although
Present invention has been described in detail with reference to the aforementioned embodiments, it will be understood by those of ordinary skill in the art that：It still may be used
With technical scheme described in the above embodiments is modified or equivalent replacement of some of the technical features；
And these modifications or replacements, various embodiments of the present invention technical solution that it does not separate the essence of the corresponding technical solution spirit and
Range.
Claims (10)
1. a kind of garden waste processing system, which is characterized in that including：
Crushing system, the crushing system are used to pending garden waste being ground into discarded composition granule；
Hybrid system, the hybrid system are used to receive the part of the discarded composition granule, and by itself and microbial inoculum, fermentation auxiliary material
It is mixed into discarded mixture；And
Fermentation system, the fermentation system include one section of fermentation system and two sections of fermentation systems；Wherein,
One section of fermentation system is fermentation half for receiving the discarded mixture, and by the discarded mixture hot fermentation
Finished product, it is garden waste tunning that two sections of fermentation systems continue fermentation to the fermentation semi-finished product.
2. garden waste processing system according to claim 1, it is characterised in that：The crushing system includes：
The pending garden waste is cut into sheet waste by level-one crushing system, the level-one crushing system；With
The sheet waste is crushed the waste for predefined size by two level crushing system, the two level crushing system
Grain.
3. garden waste processing system according to claim 1, it is characterised in that：Further include：
Carbonization system, the carbonization system are used to receive another part of the discarded composition granule, and are carbonized and are given up for gardens
Gurry charcoal；Wherein, the garden waste charcoal is used to be mixed into soil with the garden waste tunning
Conditioner.
4. garden waste processing system according to claim 3, it is characterised in that：Further include：
Discharging bin, the discharging bin include a feeding mouth and two discharge ports；Wherein, the feeding mouth and the crushing system
Outlet connection, one in the discharge port connect with the entrance of the hybrid system, in the discharge port another with
The entrance of the carbonization system connects.
5. garden waste processing system according to claim 3, it is characterised in that：The carbonization system further includes：
The outlet of exhaust gas channel, the exhaust gas channel is connect with the entrance of one section of fermentation system, is for described one section fermentation
System provides high temperature hot gas；With
Collection system, the collection system are used to collect carbonization by-product wood vinegar and wood tar that the carbonization system generates.
6. garden waste processing system according to claim 1, it is characterised in that：One section of fermentation system includes：
Fermentation roller carries out hot fermentation after the discarded mixture enters the fermentation roller in the fermentation roller.
7. garden waste processing system according to claim 1, it is characterised in that：Two sections of fermentation systems include：
Multiple distributing troughs, the fermentation semi-finished product ferment in the distributing trough；
Cloth system, the fermentation semi-finished product for being allocated in the multiple distributing trough by the cloth system.
8. garden waste processing system according to claim 7, it is characterised in that：The cloth trench bottom is equipped with aeration
Pipeline, the aeration tube road by the fermentate heap body that fermentation semi-finished product are piled into the distributing trough for providing air.
9. garden waste processing system according to claim 8, it is characterised in that：Two sections of fermentation systems also wrap
It includes：
Turner, the turner are used to stir the fermentate heap body in the distributing trough.
10. garden waste processing system according to claim 9, it is characterised in that：Two sections of fermentation systems also wrap
It includes：
Rail relayer is migrated, the rail relayer that migrates carries the turner, for driving the turner in the different cloth
It is moved between hopper.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810588649.8A CN108636992B (en) | 2018-06-08 | 2018-06-08 | Garden waste aerobic fermentation energy recycling process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810588649.8A CN108636992B (en) | 2018-06-08 | 2018-06-08 | Garden waste aerobic fermentation energy recycling process |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN108636992A true CN108636992A (en) | 2018-10-12 |
| CN108636992B CN108636992B (en) | 2023-12-01 |
Family
ID=63752174
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810588649.8A Active CN108636992B (en) | 2018-06-08 | 2018-06-08 | Garden waste aerobic fermentation energy recycling process |
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| CN115254926A (en) * | 2022-08-15 | 2022-11-01 | 杭州蓝郡农业科技有限公司 | Mobile agricultural organic waste treatment and utilization system and method |
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