CN109772864A - A kind of free of contamination house refuse aerobic fermentation system and fermentation process - Google Patents

A kind of free of contamination house refuse aerobic fermentation system and fermentation process Download PDF

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Publication number
CN109772864A
CN109772864A CN201910247201.4A CN201910247201A CN109772864A CN 109772864 A CN109772864 A CN 109772864A CN 201910247201 A CN201910247201 A CN 201910247201A CN 109772864 A CN109772864 A CN 109772864A
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aerobic fermentation
house refuse
aerobic
fermentation chamber
fermentation
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陈天虎
汪家权
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Anhui Anteji Waste Resource Research Center Co Ltd
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Anhui Anteji Waste Resource Research Center Co Ltd
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Abstract

The invention discloses a kind of free of contamination house refuse aerobic fermentation system and fermentation process, including several aerobic fermentation chambers disposed in parallel, and ventilation channel, leachate reeirculation pipeline and gas exhaust piping are provided in each fermentation cabin.Aerobic fermentation system of the invention realizes totally-enclosed aerobic fermentation, and ordorless gas is generated, is discharged without landfill leachate, improves the environment in garbage disposal site, reduce the maintenance cost of consumer waste filling and embedding processing.

Description

A kind of free of contamination house refuse aerobic fermentation system and fermentation process
Technical field
The invention belongs to Solid Waste Treatment and Resources to utilize technical field, and in particular to domestic rubbish disposal.
Background technique
Domestic waste is the solid waste having a large capacity and a wide range.It is wanted with China's socio-economic development and to environmental quality Ask higher and higher, the amount of house refuse is increasing, collect, transhipment, processing and recycling also increasingly by governments at all levels, The great attention of scientific worker.
Disposal of Domestic mode has many different group technologies.Main disposal technology is in early days with compost, natural heap Deposit, fill based on.But with the attention to soil environment quality and agricultural food product safety, producing fertilizer from refuse in daily life is because containing The poisonous and harmful substances such as heavy metal are gradually eliminated.Naturally stockpiling, simple landfill are because generating serious underground water pollution, also It is prohibited.House refuse is directly sorted and was once taken seriously, but because obstacle, operation dimension often occurs in the direct separation system of rubbish Shield is difficult, sorting product recycling benefits are not high, after especially sorting compost part fertilizer efficiency it is low, there are environmental risk, be difficult to it is outer Pin, causes directly to be sorted in China's domestic rubbish disposal and is difficult to promote.
The processing mode of house refuse mainstream is sanitation type landfill, power generation by waste combustion at present.Sanitary landfills can accomplish safety Harmlessness disposing, but refuse landfill stench is unpleasant, mosquito growth is serious, environment is dirty and messy badly, greenhouse gas emissions are huge Greatly, landfill leachate treatment it is difficult, it is at high cost be landfill yard operation and maintenance very big burden.Sanitary landfills handle one-time investment compared with Greatly, it takes up a large area, could not realize garbage as resource utilization and minimizing target.And landfill yard limited space, after the several years It after all to close, the awkward situation that house refuse can nowhere bury occurs in the selected difficulty in new site.From domestic rubbish disposal it is innoxious, From the point of view of minimizing target, incinerating method is most safe, most thorough.Meanwhile heat caused by burning process can also generate electricity.But because House refuse water content is high, calorific value is low, causes generating efficiency low.And consumer waste incineration generates dioxin, needs complicated height The flue gases purification processing of consumption is just able to satisfy emission request.It can equally be generated during the rubbish stockpiling of municipal solid waste incinerator The environmental sanitations such as stench problem and serious atmosphere polluting problem cause many incineration plant construction to be difficult to land implementation.Burn hair Electricity equally exists the problem that one-time investment is larger, operation cost is high.Therefore, refuse disposal and resource technology, which are developed, is always The hot spot in scientific and technological development field.
Aerobic fermentation is carried out to house refuse, refuse moisture, degradation organic matter can be effectively reduced, avoid at house refuse The malodor problem during the stockpiling of factory's rubbish is managed, and generating efficiency can be improved.But existing aerobic fermentation chamber is mostly open, if with this The aerobic fermentation chamber of kind form handles house refuse, and the exhaust gas that will affect its hygienic conditions, and generate during the fermentation can be made At serious atmosphere polluting problem.Therefore, the structure of existing aerobic fermentation chamber is not suitable for domestic waste disposal site.
Summary of the invention
To avoid above-mentioned existing deficiencies in the technology, the present invention provides a kind of free of contamination house refuse is good Oxygen system and fermentation process, it is intended to carry out house refuse aerobic fermentation by the means of economical and efficient, improve destructor plant Hygienic conditions.
The present invention is to realize goal of the invention, is adopted the following technical scheme that
A kind of free of contamination house refuse aerobic fermentation system, it is characterized in that: it is removed including house refuse lower hopper, biology Smelly dose of holding vessel and aerobic fermentation chamber group;
Bag-breaking machine is provided in the house refuse lower hopper;
Biological deodorant flusher, the biological deodorant sprinkling dress are additionally provided in the house refuse lower hopper It sets and the biological deodorant holding vessel is connected to by pipeline;
The aerobic fermentation chamber group is arranged in parallel by several closed aerobic fermentation chambers, the one side of the aerobic fermentation chamber Outlet portal is equipped with equipped with access doors, opposite another side;A shared public affairs are provided at the access doors of each aerobic fermentation chamber Gallery altogether;The top of the public gallery is arranged in the discharge port of the house refuse lower hopper;
Landfill leachate collecting pit is arranged in the public gallery;The ground of the aerobic fermentation chamber is in ramped shaped, Descending side is provided with intercepting gutter;The intercepting gutter confluence of each aerobic fermentation chamber is connected to the landfill leachate collecting pit;
It is equipped with ventilation channel in the bottom of each aerobic fermentation chamber, the ventilation channel is connected to oxygen supply air blower;
It is equipped with leachate reeirculation pipeline on the top of each aerobic fermentation chamber, in the landfill leachate collecting pit Immersed pump is installed;The leachate reeirculation pipeline connection is to the immersed pump;
It is equipped with gas exhaust piping at the top of each aerobic fermentation chamber, the gas exhaust piping is connected to deodorization by exhaust blower Tower.
The aerobic fermentation chamber group is that full underground or semi-underground type are arranged.
The ground of the aerobic fermentation chamber from apart from intercepting gutter farther out a side to the gradient of intercepting gutter side be 3-5%, from The gradient of outlet portal side to access doors side is 0.3-1%.
The quantity of aerobic fermentation chamber is no less than 5 in the aerobic fermentation chamber group.
The aerobic fermentation chamber in a rectangular parallelepiped shape, high 5-15m, width 5-30m, long 30-100m.
Draining channel steel is fixed in the roof two sides of the aerobic fermentation chamber.
The method for carrying out aerobic fermentation using the house refuse aerobic fermentation system, includes the following steps:
Step 1 is stored in biological deodorant in the biological deodorant holding vessel;
House refuse is poured into house refuse lower hopper, packaging bag is scratched by bag-breaking machine, and sprayed and filled by biological deodorant It sets and sprays biological deodorant into house refuse lower hopper, keep biological deodorant uniform with domestic garbage mixing;
Step 2 is added to the house refuse blanking of biological deodorant to public gallery, then successively moves into each aerobic fermentation Storehouse, each aerobic fermentation chamber laying close fermentation cabin access doors after buying securities with all one's capital, start to be laid with next aerobic fermentation chamber;
Step 3, from oxygen supply air blower by ventilation channel buy securities with all one's capital to laying after aerobic fermentation chamber in be continually fed into air, The landfill leachate dissolved oxygen that air capacity is passed through to flow out in aerobic fermentation chamber is greater than 0.5mg/L as control parameter, to maintain Oxygen condition starts static fermentation;
Each aerobic fermentation chamber is then pooled to rubbish after the landfill leachate gravity flow that fermentation process generates is pooled to intercepting gutter Rubbish leachate collection pool;
First 5 days of fermentation are sprayed from leachate reeirculation pipeline into aerobic fermentation chamber at interval of 4h by immersed pump Landfill leachate, persistently sprays 1h every time, to maintain moisture needed for the fermentation of house refuse heap body in aerobic fermentation chamber;It is quiet Stop spray after setting fermentation 5 days, continue fermentation 5-10 days, makes biomass organic matter degradation in house refuse, decomposed, stable, make Moisture evaporation, obtains decomposed material after loose, odorless fermentation;
Exhaust gas caused by aerobic fermentation chamber fermentation process is extracted out by exhaust blower from gas exhaust piping, is sent to deodorizing tower Deodorization;
Each aerobic fermentation chamber independently carries out aerobic fermentation;
Step 4 stops ventilation after fermentation, opens the outlet portal of aerobic fermentation chamber, clears out decomposed material after fermentation.
Further, the additional amount of biological deodorant described in step 1 is rubbish 0.5-5kg per ton.
Further, decomposed material is combined and is sorted by screening, electromagnetic separation and selection by winnowing after gained fermentation, is sub-elected Fertile soil, wooden, rubber, fabric, metal, plastics, glass, ceramics, brick and tile and stone;
Gained fertile soil is used as stock growing greening nutritive soil;Gained metal, which is sent to smeltery, to be regenerated;The washing of gained plastics Being granulated after drying becomes regenerated plastics master batch;Gained glass, ceramics, brick and tile and stone are used as construction material;Gained is wooden, rubber Glue, fabric are used as fuel thermal decomposition gasification or directly the burning recycling energy.
The beneficial effects of the present invention are embodied in:
1, aerobic fermentation system of the invention is purified by complete alternation to waste water, to the deodorization of exhaust gas, realizes waste water And zero waste gas emission, eliminate the malodor problem of domestic waste disposal site;And in the present invention aerobic fermentation chamber be it is semi-underground even The totally-enclosed system of full underground, avoids foul gas loss welding, it is dirty and messy smelly to completely solve domestic waste disposal site Awkward situation improves the environmental sanitation situation of domestic garbage treatment plant.
2, the present invention sprays biological deodorant into house refuse, it is possible to reduce the production of foul gas before aerobic fermentation It is raw.
3, landfill leachate collecting pit is arranged in the present invention under public gallery, and the setting of aerobic fermentation chamber ground is sloping Shape, the landfill leachate that fermentation process can be made to generate flow automatically to landfill leachate collecting pit, on the one hand facilitate junk-heap body It drains away the water, ultimately helps the water content for reducing matured waste;On the other hand facilitate the sprinkling irrigation processing of landfill leachate.
4, method and system of the invention carries out complete alternation processing to landfill leachate, aerobic fermentation early period to life The landfill leachate that sprinkling irrigation aerobic fermentation process generates in junk-heap body, aerobic fermentation later period no longer spray, moisture evaporation decrement, The processing of landfill leachate is realized, to realize the zero-emission of waste water, eliminates the problem of landfill leachate treatment, disposition. And the recharge of landfill leachate, a large amount of thermophilic aerobic microbiologicals are vaccinated with for junk-heap body fermentation, accelerate the micro- life of junk-heap body Object growth rate accelerates aerobic microbiological proliferation and metabolism and organic matter degradation speed, improves the fermentation temperature of junk-heap body, can So that the raising of junk-heap body temperature reaches 80 DEG C or more, rapid high-temperature aerobic fermentation is realized, most of pathogenic bacteria can be inactivated And weed seed, good condition is created for utilization humous after fermentation.
5, after carrying out aerobic fermentation to house refuse by means of the present invention, have and further divided using to it Choosing, avoids the problem that house refuse directly sorts: anaerobism has been smelly for the rubbish shipped from residential block, water content Height is adhered seriously, and directly sorting is difficult, and foul gas diverging seriously, it is relatively difficult to control foul gas pollution.First aerobic fermentation The mode sorted afterwards has the following advantages: reducing refuse moisture, is significantly reduced, reduces sorting load and cost;It is degradable to have The corruption of machine matter stabilizes, grain refined;All kinds of materials are easier to dispersion, depolymerization, sorting in rubbish;The material clamp band impurity of sorting is few, It is easier to be further processed.
6, after being fermented by means of the present invention, then house refuse is sorted, the wholly-owned source of solid waste may be implemented Change.
Detailed description of the invention
Fig. 1 is the floor map of life rubbish aerobic fermentation system;
Fig. 2 is the schematic cross section of aerobic fermentation chamber group;
Figure label: 1 is house refuse lower hopper;2 be biological deodorant holding vessel;3 be aerobic fermentation chamber;4 be public Gallery;5 be landfill leachate collecting pit;6 be intercepting gutter;7 be ventilation channel;8 be oxygen supply air blower;9 return for landfill leachate Fill pipeline;10 be immersed pump;11 be bag-breaking machine;12 be biological deodorant flusher;13 be gas exhaust piping;14 be exhaust air blast Machine;15 be deodorizing tower;16 be ground;3A fermentation cabin roof;3B is fermentation cabin concrete wall;3C is fermentation warehouse partition.
Specific embodiment
In order to make the foregoing objectives, features and advantages of the present invention clearer and more comprehensible, below with reference to embodiment to this hair Bright specific embodiment is described in detail.The following contents is only to design example of the invention and explanation, institute Belong to those skilled in the art to make various modifications or additions to the described embodiments or using similar Mode substitutes, and as long as it does not deviate from the concept of invention or beyond the scope defined by this claim, should belong to the present invention Protection scope.
As depicted in figs. 1 and 2, a kind of free of contamination house refuse aerobic fermentation system, including house refuse lower hopper 1, biological deodorant holding vessel 2 and aerobic fermentation chamber group.
It is provided with bag-breaking machine 11 in house refuse lower hopper 1, is used for Domestic garbage bag-breaking, blanking.In specific implementation, The disposable type of achievable required function or the bag-breaking machine of structure can be used in bag-breaking machine.
Biological deodorant flusher 12, biological deodorant flusher 12 are additionally provided in house refuse lower hopper 1 Biological deodorant holding vessel 2 is connected to by pipeline;Biological deodorant flusher be used for Domestic garbage bag-breaking, blanking it is same When, biological deodorant is sprayed into house refuse, keeps biological deodorant uniform with domestic garbage mixing.In specific implementation, biology The structure of existing any achievable required function can be used in deodorant flusher, such as can be by force (forcing) pump, transfer pipeline, flow Meter, flow control valve, sprinkler composition, effect is to add biological deodorizing into house refuse to be processed according to required measure Agent.
Aerobic fermentation chamber group is arranged in parallel by several closed aerobic fermentation chambers 3, the one side of aerobic fermentation chamber 3 be equipped with into Mouth door, opposite another side are equipped with outlet portal;A shared public gallery is provided at the access doors of each aerobic fermentation chamber 3 4;The top of public gallery 4 is arranged in the discharge port of house refuse lower hopper 1;House refuse passes through weight by house refuse lower hopper It after power direct blanking to public gallery, then successively send to each aerobic fermentation chamber, in specific implementation, rubbish can be set on public gallery Rubbish conveying device is successively sent house refuse to each aerobic fermentation chamber by waste conveyor.
Landfill leachate collecting pit 5 is provided with below public gallery 4;The ground of aerobic fermentation chamber 3 is in ramped shaped, direction The direction of the landfill leachate collecting pit 5 tilts, and descending side is provided with intercepting gutter 6;The intercepting gutter 6 of each aerobic fermentation chamber converges Stream is connected to landfill leachate collecting pit 5, so that after the landfill leachate gravity flow that fermentation process generates is pooled to intercepting gutter, then It is pooled to landfill leachate collecting pit.In specific implementation, with the parallel direction with public gallery 4 be laterally, with from outlet portal to The direction of access doors be it is longitudinal, the ground of aerobic fermentation chamber from apart from intercepting gutter farther out gradient from a side to intercepting gutter side (i.e. Lateral gradient) be 3-5%, gradient from outlet portal side to access doors side (i.e. longitudinal gradient) is 0.3-1%.
It is equipped with ventilation channel 7 in the bottom of each aerobic fermentation chamber 3, ventilation channel 7 is connected to oxygen supply air blower 8, oxygen supply Air blower conveys air into aerobic fermentation chamber by ventilation channel, to maintain the aerobic gaseous environment in aerobic fermentation chamber.Tool During body is implemented, ventilation channel is perforated pipe, for discharging gas.
It is equipped with leachate reeirculation pipeline 9 on the top of each aerobic fermentation chamber 3, in landfill leachate collecting pit 5 Immersed pump 10 is installed;Leachate reeirculation pipeline 9 is connected to immersed pump 10.Garbage filter in landfill leachate collecting pit Liquid is sprayed on demand by leachate reeirculation pipeline into the house refuse heap body in each aerobic fermentation chamber.In specific implementation, Suitable construction can be arranged according to aerobic fermentation chamber size in leachate reeirculation pipeline, can be uniform by landfill leachate with guarantee The house refuse to all areas is sprayed, such as can be used and several cross-perforating pipes are set under supervisor, then adds the side of spray head Formula.
It is equipped with gas exhaust piping 13 at the top of each aerobic fermentation chamber 3, gas exhaust piping 13 is connected to by exhaust blower 14 Deodorizing tower 15.In specific implementation, deodorizing tower can be the deodorizing tower of the existing arbitrary structures that can reach required deodorizing effect.
Aerobic fermentation chamber group is that (as shown in Fig. 2, being semi-underground type) is arranged in full underground or semi-underground type.In specific implementation, The construction method of aerobic fermentation chamber are as follows: garbage disposal place size is determined according to the amount of receiving house refuse, selected flat The position that aerobic fermentation chamber is cooked up on whole place digs out the earthwork in the position for supporting fermentation cabin well, sets the rubbish of fermentation cabin Entrance and exit is then divided into partition with two face wall of concreting (fermentation cabin concrete wall 3B as shown in Figure 2) Several parallel warehouses (fermentation warehouse partition 3C as shown in Figure 2) of rectangular-shape, and entrance door is installed for each warehouse And outlet portal.In the longitudinally fixed draining channel steel in the roof two sides of each aerobic fermentation chamber, the fixed girder steel in channel steel two sides constructs room Frame, roof, then (fermentation cabin roof 3A as shown in Figure 2) is covered with required material at top, make each aerobic fermentation chamber structure At closed space.The volume of each aerobic fermentation chamber is arranged on demand, can preferably accommodate 3~5 days house refuse amouns, such as each Warehouse may be configured as high 5-15m, width 5-30m, long 30-100m.Entire garbage disposal site configures aerobic fermentation chamber 5 or more (such as Fig. 1, it is 5 shown in 2), periodically rotation charging, fermentation, discharging uses, with specific reference to receiving quantity of refuse configuration.The row on roof Sink steel is used as gutter and maintenance walkway simultaneously, exports rain water on roof, snow-broth to tank.
In specific implementation, the lower section of public 4 center of gallery is arranged in landfill leachate collecting pit 5, in garbage filter Covering on liquid collecting pit 5 and intercepting gutter 6 has latticed comb water plate;The depth of intercepting gutter is 10-20cm.
In specific implementation, public gallery can be configured to ramped shaped and be connected with ground, both convenient for the wheeled machine for transporting The disengaging of tool equipment, and rainwater is avoided to flow into public gallery.
Green plants layer can be set on the roof of aerobic fermentation chamber.In specific implementation: can be in the storehouse of aerobic fermentation chamber The fertile soil of 20-40cm thickness is covered on top, thereon Turf Culture;Or pot flowers nursery stock is put in the silo roof of aerobic fermentation chamber Greening.Green plants layer can beautify the environment.
In specific implementation, commercially available any a, preferably configuration as follows: by fresh life is can be used in biological deodorant After the fermentation obtained by the aerobic fermentation of rubbish living and house refuse decomposed material according to mass ratio 2:1~4 after mixing, with 2~ 10 times of water elution, obtains leachate;The leachate is uniformly mixed with saccharomycete according to mass ratio 1000:1~10, is obtained It is inoculated with bacterium solution;Organic matter plus water are configured to the organic matter culture medium that mass concentration is 1~5%;Then bacterium solution will be inoculated with and had After the 1~10:100 mixing by volume of machine object culture medium, add occupy machine amount of substance 1~10% ferriferous oxide mixing it is equal Even, ferment 24~48h, obtains biological deodorant.Wherein, the organic matter for preparing culture medium is brown sugar, sucrose, glucose, lactic acid At least one of salt, acetate, beef extract, molasses water, kitchen garbage or livestock waste, nano-iron oxide are by commercially available iron Oxide or natural nano ferriferous oxide ore (such as oolitic hematite, limonite) crush the following powder of 100 mesh obtained.It is above-mentioned Microorganism adds yeast in decomposed object after biological deodorant is fermented by the microorganism in Fresh Life rubbish, aerobic fermentation gained Bacterium, ferriferous oxide enrichment culture are made.Microorganism therein is all indigenous microorganism, adapts to home environment;Ferriferous oxide with it is micro- Biotic interactions improves microbial metabolism microenvironment, improves activity, improves the speed of decomposing organic matter;Biological deodorant packet Containing amphimicrobe, facultative aerobe, aerobic bacteria, acts synergistically with the saccharomycete of addition, eliminate the foul odour substance in rubbish;And Biological deodorant includes the microorganism for being suitable for fast breeding at various temperatures, and after being added in junk-heap body, junk-heap body increases Peak temperature that is warm fast, reaching is high, biomass corruption stablize it is fast, rubbish fermentation is greatly shortened needed for the time.
The method for carrying out aerobic fermentation using above-mentioned house refuse aerobic fermentation system, includes the following steps:
Step 1 is stored in biological deodorant in biological deodorant holding vessel 2;
House refuse is poured into house refuse lower hopper 1, packaging bag is scratched by bag-breaking machine 11, and sprayed by biological deodorant Device 12 sprays biological deodorant into house refuse lower hopper, keeps biological deodorant uniform with domestic garbage mixing;Biology removes Smelly dose of additional amount is rubbish 0.5-5kg per ton;
Step 2 is added to the house refuse blanking of biological deodorant to public gallery 4, then successively moves into each aerobic hair Ferment storehouse 3, each aerobic fermentation chamber laying close fermentation cabin access doors after buying securities with all one's capital, start to be laid with next aerobic fermentation chamber;
Step 3, from oxygen supply air blower 8 by ventilation channel 7 buy securities with all one's capital to laying after aerobic fermentation chamber in be continually fed into sky Gas, to maintain aerobic state to start static fermentation, the landfill leachate dissolved oxygen that is passed through air capacity to flow out in aerobic fermentation chamber It is control parameter greater than 0.5mg/L;
Each aerobic fermentation chamber is then pooled to after the landfill leachate gravity flow that fermentation process generates is pooled to intercepting gutter 6 Landfill leachate collecting pit 5;
First 5 days of fermentation are sprayed from leachate reeirculation pipeline 9 into aerobic fermentation chamber at interval of 4h by immersed pump 10 A landfill leachate is drenched, persistently sprays 1h every time, to maintain moisture needed for the fermentation of house refuse heap body in aerobic fermentation chamber; Standing for fermentation stops spray after 5 days, continue fermentation 5-10 days, makes biomass organic matter degradation in house refuse, decomposed, stable, Moisture is evaporated, decomposed material after loose, odorless fermentation is obtained;
Exhaust gas caused by aerobic fermentation chamber fermentation process is extracted out by exhaust blower 14 from gas exhaust piping 13, is sent to removing Smelly 15 deodorization of tower;
Each aerobic fermentation chamber independently carries out aerobic fermentation;
Step 4 stops ventilation after fermentation, opens the outlet portal of aerobic fermentation chamber, clears out decomposed material after fermentation.
Decomposed material is combined and is sorted by screening, electromagnetic separation and selection by winnowing after step 5, gained fermentation, is sub-elected Fertile soil, wooden, rubber, fabric, metal, plastics, glass, ceramics, brick and tile and stone;
Gained fertile soil is used as stock growing greening nutritive soil;Gained metal, which is sent to smeltery, to be regenerated;The washing of gained plastics Being granulated after drying becomes regenerated plastics master batch;Gained glass, ceramics, brick and tile and stone are used as construction material;Gained is wooden, rubber Glue, fabric are used as fuel thermal decomposition gasification or directly the burning recycling energy.

Claims (9)

1. a kind of free of contamination house refuse aerobic fermentation system, it is characterised in that: including house refuse lower hopper (1), biology Deodorant holding vessel (2) and aerobic fermentation chamber group;
Bag-breaking machine (11) are provided in the house refuse lower hopper (1);
It is additionally provided with biological deodorant flusher (12) in the house refuse lower hopper (1), the biological deodorant spray It spills device (12) and the biological deodorant holding vessel (2) is connected to by pipeline;
The aerobic fermentation chamber group is arranged in parallel by several closed aerobic fermentation chambers (3), and the one of the aerobic fermentation chamber (3) Face is equipped with access doors, opposite another side is equipped with outlet portal;One is provided at the access doors of each aerobic fermentation chamber (3) to share Public gallery (4);The discharge port of the house refuse lower hopper (1) is arranged in the top of the public gallery (4);
Landfill leachate collecting pit (5) are arranged in the public gallery (4);The ground of the aerobic fermentation chamber (3) is in oblique Ramp shaped, descending side are provided with intercepting gutter (6);Intercepting gutter (6) confluence of each aerobic fermentation chamber is connected to the landfill leachate Collecting pit (5);
It is equipped with ventilation channel (7) in the bottom of each aerobic fermentation chamber (3), the ventilation channel (7) is connected to oxygen supply air blower (8);
Leachate reeirculation pipeline (9) are equipped on the top of each aerobic fermentation chamber (3), in the landfill leachate collecting pit (5) immersed pump (10) are installed in;The leachate reeirculation pipeline (9) is connected to the immersed pump (10);
Gas exhaust piping (13) are equipped at the top of each aerobic fermentation chamber (3), the gas exhaust piping (13) passes through exhaust blower (14) deodorizing tower (15) are connected to.
2. a kind of free of contamination house refuse aerobic fermentation system according to claim 1, it is characterised in that: described aerobic Fermentation cabin group is that full underground or semi-underground type are arranged.
3. a kind of free of contamination house refuse aerobic fermentation system according to claim 1, it is characterised in that: described aerobic The ground of fermentation cabin from apart from intercepting gutter farther out a side to the gradient of intercepting gutter side be 3-5%, from outlet portal side to import The gradient of door side is 0.3-1%.
4. a kind of free of contamination house refuse aerobic fermentation system according to claim 1, it is characterised in that: described aerobic The quantity of aerobic fermentation chamber is no less than 5 in fermentation cabin group.
5. a kind of free of contamination house refuse aerobic fermentation system according to claim 1, it is characterised in that: described aerobic Fermentation cabin in a rectangular parallelepiped shape, high 5-15m, width 5-30m, long 30-100m.
6. a kind of free of contamination house refuse aerobic fermentation system according to claim 1, it is characterised in that: described good The roof two sides in aerobe fermentation storehouse are fixed with draining channel steel.
7. a kind of carry out aerobic fermentation using house refuse aerobic fermentation system described in any one of claim 1~6 Method, which comprises the steps of:
Step 1 is stored in biological deodorant in the biological deodorant holding vessel (2);
House refuse is poured into house refuse lower hopper (1), packaging bag is scratched by bag-breaking machine (11), and sprayed by biological deodorant Device (12) sprays biological deodorant into house refuse lower hopper, keeps biological deodorant uniform with domestic garbage mixing;
Step 2 is added to the house refuse blanking of biological deodorant to public gallery (4), then successively moves into each aerobic fermentation Storehouse (3), each aerobic fermentation chamber laying close fermentation cabin access doors after buying securities with all one's capital, start to be laid with next aerobic fermentation chamber;
Step 3, from oxygen supply air blower (8) by ventilation channel (7) buy securities with all one's capital to laying after aerobic fermentation chamber in be continually fed into sky Gas, the landfill leachate dissolved oxygen for being passed through air capacity to flow out in aerobic fermentation chamber are greater than 0.5mg/L as control parameter, to maintain Aerobic state starts static fermentation;
Each aerobic fermentation chamber is then pooled to rubbish after the landfill leachate gravity flow that fermentation process generates is pooled to intercepting gutter (6) Rubbish leachate collection pool (5);
First 5 days of fermentation are sprayed from leachate reeirculation pipeline (9) into aerobic fermentation chamber at interval of 4h by immersed pump (10) A landfill leachate is drenched, persistently sprays 1h every time, to maintain moisture needed for the fermentation of house refuse heap body in aerobic fermentation chamber; Standing for fermentation stops spray after 5 days, continue fermentation 5-10 days, makes biomass organic matter degradation in house refuse, decomposed, stable, Moisture is evaporated, decomposed material after loose, odorless fermentation is obtained;
Exhaust gas caused by aerobic fermentation chamber fermentation process is extracted out by exhaust blower (14) from gas exhaust piping (13), is sent to removing Smelly tower (15) deodorization;
Each aerobic fermentation chamber independently carries out aerobic fermentation;
Step 4 stops ventilation after fermentation, opens the outlet portal of aerobic fermentation chamber, clears out decomposed material after fermentation.
8. according to the method described in claim 7, it is characterized by: the additional amount of biological deodorant described in step 1 is per ton Rubbish 0.5-5kg.
9. according to the method described in claim 7, it is characterized by: gained fermentation after decomposed material by screening, electromagnetic separation and Selection by winnowing, which combines, to be sorted, sub-elect fertile soil, wooden, rubber, fabric, metal, plastics, glass, ceramics, brick and tile and Stone;
Gained fertile soil is used as stock growing greening nutritive soil;Gained metal, which is sent to smeltery, to be regenerated;Gained plastics wash drying Being granulated afterwards becomes regenerated plastics master batch;Gained glass, ceramics, brick and tile and stone are used as construction material;Gained is wooden, rubber, fibre It ties up fabric and is used as fuel thermal decomposition gasification or directly the burning recycling energy.
CN201910247201.4A 2019-03-29 2019-03-29 A kind of free of contamination house refuse aerobic fermentation system and fermentation process Pending CN109772864A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110560461A (en) * 2019-09-29 2019-12-13 安徽安特治废弃物资源化研究中心有限公司 box-shaped push-type domestic garbage continuous aerobic fermentation system and application method thereof
CN111570467A (en) * 2020-04-30 2020-08-25 南京大学 Ectopic aerobic reinforced stabilization system and method for stored household garbage
WO2022233259A1 (en) * 2021-05-06 2022-11-10 南京大学 Container equipment for closed transportation and ectopic aerobic stabilization of stock garbage and method therefor

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007054764A (en) * 2005-08-26 2007-03-08 Kyowa Kako Kk Continuous drying type biomass gasification plant
CN102180719A (en) * 2010-12-08 2011-09-14 中国农业大学 Decomposition device for treating rural domestic waste composting waste gas with biomass
CN103447279A (en) * 2013-07-30 2013-12-18 浙江大学 Household garbage treatment method and treatment equipment
CN109396161A (en) * 2018-12-17 2019-03-01 深圳市三林生物科技工程有限公司 The quick volume reduction decrement of crude waste and the method for comprehensive resource processing
CN209697699U (en) * 2019-03-29 2019-11-29 安徽安特治废弃物资源化研究中心有限公司 A kind of free of contamination house refuse aerobic fermentation system

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007054764A (en) * 2005-08-26 2007-03-08 Kyowa Kako Kk Continuous drying type biomass gasification plant
CN102180719A (en) * 2010-12-08 2011-09-14 中国农业大学 Decomposition device for treating rural domestic waste composting waste gas with biomass
CN103447279A (en) * 2013-07-30 2013-12-18 浙江大学 Household garbage treatment method and treatment equipment
CN109396161A (en) * 2018-12-17 2019-03-01 深圳市三林生物科技工程有限公司 The quick volume reduction decrement of crude waste and the method for comprehensive resource processing
CN209697699U (en) * 2019-03-29 2019-11-29 安徽安特治废弃物资源化研究中心有限公司 A kind of free of contamination house refuse aerobic fermentation system

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110560461A (en) * 2019-09-29 2019-12-13 安徽安特治废弃物资源化研究中心有限公司 box-shaped push-type domestic garbage continuous aerobic fermentation system and application method thereof
CN110560461B (en) * 2019-09-29 2024-02-09 安徽安特治废弃物资源化研究中心有限公司 Box-shaped pushing type domestic garbage continuous aerobic fermentation system and application method thereof
CN111570467A (en) * 2020-04-30 2020-08-25 南京大学 Ectopic aerobic reinforced stabilization system and method for stored household garbage
CN111570467B (en) * 2020-04-30 2021-11-16 南京大学 Ectopic aerobic reinforced stabilization system and method for stored household garbage
WO2022233259A1 (en) * 2021-05-06 2022-11-10 南京大学 Container equipment for closed transportation and ectopic aerobic stabilization of stock garbage and method therefor

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