A kind of organic waste composting treatment method
Technical field
The present invention relates to a kind of organic waste composting treatment method, belong to technical field of garbage disposal.
Background technology
As the horizontal quickening of Chinese Urbanization and the continuous improvement for the treatment of rate of domestic sewage, caused organic waste are also got over
Come more, a main part shows that sludge quantity sharply increases caused by sewage disposal process in organic waste.However, due to lacking
Weary rationally effective management method and processing disposal technology, a large amount of municipal sludges can only be stacked temporarily, thus caused secondary dirt
Contaminate and huge harm is brought to environment, seek rational processing treatment approach and asked as countries in the world letter focus to be solved
Topic.
Aerobic fermentation refers to utilize aerobic bacteria and oxygen, sludge high temperature is fermented, and it is processing and disposal municipal sludge
A kind of cost-effective good method, have the advantages that to make organic nuisance complete decomposition, control well.It uses multidisciplinary skill
Art, multiphase organic matter is decomposed in specific environment using microbiologic population, the humus by improving sludge into stabilization,
Often it is divided into three phases for infertile field or soil improvement, Composting Process:First stage is middle thermophase, and second stage is high temperature
Stage, phase III are the decomposed stages.The mark that middle thermophase terminates is heap temperature rise to 45 DEG C, hot stage OUR is high,
Temperature is high, volatile organic matter degradation rate is high, stink is dense;Then temperature was low, OUR is low the decomposed stage, voidage increases
Greatly, humus increases and stabilized.Aerobic compost is innoxious will to ensure that stack layers temperature is maintained above 5-7 days at 55 DEG C, to reach
The requirement of relation by marriage worm's ovum and Escherichia coli is killed, therefore whole processing procedure gets off to need altogether the time of ten days or so.
For the living environment that current house refuse is increasing, air and environmental quality requirement are strict, traditional place
The reason process cost time is longer, and treatment effeciency is relatively low, causes pending rubbish or solid waste pilling up time to grow, and heap
Caused stink is difficult to handle in fertile course of reaction, influences ecological environment, or processing needs to spend many resources, cost compared with
It is high.
Therefore, for developing a kind of new organic waste compost method, not only with urgent researching value, it may have good
Good economic benefit and commercial application potentiality, this is exactly where the power that the present invention is accomplished and basis.
The content of the invention
The defects of in order to overcome existing organic garbage composting device as indicated above, the present inventor is goed deep into this
Research, after a large amount of creative works have been paid, so as to complete the present invention.
Specifically, the technical problems to be solved by the invention are:One kind is provided and uses new organic garbage composting device
Composting treatment method, methods described shortens processing time, improves treatment effeciency, reduce place by using the device
Manage cost.
In order to solve the above technical problems, the technical scheme is that:There is provided a kind of using organic garbage composting device
Composting treatment method, wherein the organic garbage composting device includes frame, the frame is provided with feed bin, the feed bin top
Provided with charging aperture, vertical baffle and lateral partitions are provided with the feed bin, the feed bin is divided into transverse direction by the vertical baffle
The discharging surge bunker and fermentation cabin of distribution, the discharging surge bunker bottom are provided with discharging opening, and the charging aperture is for the fermentation
Bin location, the lateral partitions are provided with some liquid-leadage holes, and the fermentation cabin connects sepage storage silo by liquid-leadage hole, described to ooze
Liquid storage bin is rotatablely equipped with two and is used to convey material by the fermentation cabin below the fermentation cabin on the feed bin
To the spiral conveying roller of the discharging surge bunker, two spiral conveyings roll out row and set and be all connected with the first power set;
The agitating roller driven by the second power set is rotatablely equipped with the fermentation cabin, the axis of the spiral conveying roller stirs with described
The axis for mixing roller is vertically arranged, and the agitating roller is provided with axially extending fluid flow paths, and the fluid flow paths connect
Hydrogen peroxide pumping line is connect, the agitating roller is provided with some fluid holes for radially extending and connecting the fluid flow paths;
The corresponding discharging surge bunker and fermentation bin location are provided with some waste gas outlets at the top of the feed bin, and each waste gas outlet is equal
Gas path pipe is connected by a bronchus, the gas path pipe connects emission-control equipment, and the gas path pipe is provided with vacuum
Pump;The sepage storage silo bottom exports provided with sepage, the sepage outlet wastewater treatment equipment;The first power dress
Put, the second power set, vavuum pump are all connected with control unit;
The processing method is specially:It is 5- by municipal sludge and quality moisture content that quality moisture content is 60-90%
20% solid organic castoff, according to 2-4:1 mass ratio is added to by charging aperture in the fermentation cabin of the composting device,
Charging aperture is closed, opens electric-control stop valve, starts vavuum pump so that 10-20KPa negative pressure is formed in fermentation cabin, is then shut off
Electric-control stop valve, start variable-frequency motor and drive agitating roller to rotate, be warming up to 40-60 DEG C, add hydrogen peroxide, stir 20-28 hours,
When temperature reaches 70 DEG C, kept for 1-2 days at such a temperature, so as to complete the processing.
In the composting treatment method of the present invention, the quality moisture content of the municipal sludge is 60-90%, such as can
For 60%, 70%, 80% or 90%.
In the composting treatment method of the present invention, the solid organic castoff for example can be feces of livestock and poultry, kitchen
Rubbish, plant rod straw etc., its quality moisture content are 5-20%, such as can be 5%, 10%, 15% or 20%.
In the composting treatment method of the present invention, the amount of hydrogen peroxide is added, gained after stirring one day should be caused
Quality moisture content is 55-65%, C/N 30 in mixed material, wherein C/N refer to carbon containing and nitrogenous quality in mixed material it
Than.
In the composting treatment method of the present invention, as an improvement, if carrier of oxygen in fermentation cabin in processing procedure
Product concentration is less than 15%, such as less than 10%, less than 5%, then by spiral conveying roller supplemental oxygen, until the internal pressure of fermentation cabin 6
Power is higher than 20KPa, preferably above 25KPa, most preferably higher than 30KPa.
In the composting treatment method of the present invention, as an improvement, it is equipped with the every spiral conveying roller
Axially extending air ventilation passage, the air ventilation passage connect oxygen pumping line, and the spiral conveying roller is provided with
Some ventholes for radially extending and connecting the air ventilation passage.
In the composting treatment method of the present invention, as a further improvement, the venthole includes setting gradually
Inlet end, throughput and outlet side, the inlet end and outlet side are taper, and the throughput is tubular, the air inlet
The outside diameter at end is more than the diameter of the throughput, and the outside diameter of the outlet side is more than the diameter of the throughput, institute
The small end for stating inlet end and outlet side connects with the throughput.
In the composting treatment method of the present invention, as an improvement, the sepage storage silo bottom is provided with gas
Blowback cleaning device, the blow-back cleaning device include being installed on the feed bin and connect entering for the sepage storage silo
Tracheae, the air inlet pipe connect an air blower, and the air blower passage time relay connects described control unit.
In the composting treatment method of the present invention, as an improvement, TEMP is installed in the fermentation cabin
Device and oxygen concentration sensor, the temperature sensor and oxygen concentration sensor are all connected with described control unit.
In the composting treatment method of the present invention, as an improvement, the bronchus is provided with electric-control stop valve,
The electric-control stop valve connects described control unit.
In the composting treatment method of the present invention, as a further improvement, the emission-control equipment includes useless
Gas disposal tower, the exhaust-gas treatment tower bottom are provided with Sewage outlet, and the exhaust-gas treatment top of tower is provided with clean gas floss hole,
The waste gas inlet for connecting the gas path pipe is provided with above the Sewage outlet, the top of the waste gas inlet is provided with spray
Deodoriser is drenched, the close clean gas floss hole position is provided with dry powder deodoriser above the spray deodoriser.
In the composting treatment method of the present invention, as a further improvement, the spray deodoriser includes connection
The shower of deodorant liquid pumping line, the shower extend radially to the exhaust gas treating tower along the exhaust gas treating tower
Interior, the shower is provided with some shower nozzles;The dry powder deodoriser includes the housing being arranged in the exhaust gas treating tower, institute
State housing and be provided with some circuitous channels, described circuitous channel one end connects waste gas inlet, and the other end connects clean gas discharge
Mouthful, the housing is provided with some suckings connected with the circuitous channel, and deodorant powder is provided with the housing.
In the composting treatment method of the present invention, as a further improvement, the gas path pipe is tilted and is installed on
On the exhaust gas treating tower, the waste gas inlet is towards the exhaust-gas treatment tower bottom.
In the composting treatment method of the present invention, as a further improvement, the Sewage outlet gives up with described
Water treatment facilities is connected.
After employing above-mentioned processing method, present invention produces following beneficial effect:
1. due to being provided with agitating roller in fermentation cabin, and agitating roller adds hydrogen peroxide while stirring so that organic waste exists
Obtain being sufficiently mixed oxidation in whipping process, avoid and be deposited to the defects of bottom generation accumulation is difficult to oxidation, substantially reduce
The reaction time of middle thermophase and hot stage;
2. due to having used vavuum pump, ensure certain negative pressure in feed bin in middle thermophase and hot stage, with traditional work
Skill compares, and at the same reaction temperature, no matter in middle thermophase, hot stage or decomposed stage, all substantially reduces
Reaction time;Organic waste is handled using the device, it is necessary to time of 5 days or so can just complete, and is improved by about one time
Treatment effeciency, substantially reduce time of stacking garbage.
3. because spiral conveying roller connects oxygen pumping line, when oxygen concentration reduces in fermentation cabin, can mend in time
It is oxygenated, for organic waste aerobic reaction, and oxygen supplies inside fermentation cabin so that rubbish fully contacts with oxygen,
So as to reduce further processing time.
4. because the venthole on spiral conveying roller is shaped to big at both ends and small in middle so that material is neither easy to block
Venthole, oxygen is enabled to spray at a high speed again.
5. because sepage storage silo bottom is provided with blow-back cleaning device, when the liquid-leadage hole in lateral partitions is blocked
When, sepage speed will be influenceed, can now use blow-back cleaning device, blocked liquid-leadage hole is washed open, further carried
High treatment effeciency.
6. due to controlling suitable hydrogen peroxide addition, so as to accelerate process, handling process is optimized.
Brief description of the drawings
Fig. 1 is the structural representation of the embodiment of the present invention;
Fig. 2 is the arrangement schematic diagram of the spiral conveying roller and agitating roller in the embodiment of the present invention;
Fig. 3 is the structural representation of venthole in the embodiment of the present invention;
Fig. 4 is the structural representation of wastewater treatment equipment in the embodiment of the present invention.
Wherein, in figures 1-4, each number designation refers to following concrete meaning, element and/or part respectively.
In figure:1st, frame, 2, feed bin, 3, vertical baffle, 4, lateral partitions, 5, discharging surge bunker, 6, fermentation cabin, 7, sepage
Storage silo, 8, discharging opening, 9, charging aperture, 10, waste gas outlet, 11, emission-control equipment, 111, exhaust gas treating tower, 112, clean
Gas floss hole, 113, Sewage outlet, 114, gas path pipe, 115, deodorant liquid pumping line, 116, shower, 117, shower nozzle,
118th, housing, 119, circuitous channel, 12, sepage outlet, 13, wastewater treatment equipment, 14, electric-control stop valve, 15, time relay
Device, 16, air blower, 17, filter, 18, air inlet pipe, 19, motor, 20, spiral conveying roller, 201, air ventilation passage,
202nd, venthole, 2021, inlet end, 2022, throughput, 2023, outlet side, 21, agitating roller, 211, agitating shaft, 212, stirring
Blade, 213, fluid flow paths, 214, fluid hole, 22, vavuum pump, 23, swivel joint, 24, temperature sensor, 25, oxygen
Concentration sensor.
Embodiment
The present invention is further described with reference to the accompanying drawings and examples.But the purposes and mesh of these exemplary embodiments
Be only used for enumerate the present invention, any type of any restriction not is formed to the real protection scope of the present invention, it is more non-to incite somebody to action this
The protection domain of invention is confined to this.
As shown in Figure 1, Figure 2, shown in common in Fig. 3 and Fig. 4, the invention provides a kind of heap using organic garbage composting device
Fertile processing method, wherein the organic garbage composting device mainly includes frame 1, frame 1 is provided with feed bin 2, and the top of feed bin 2 is set
There is charging aperture 9, be provided with vertical baffle 3 and lateral partitions 4 in feed bin 2, feed bin 2 is divided into going out for cross direction profiles by vertical baffle 3
Expect surge bunker 5 and fermentation cabin 6, discharging surge bunker 5 bottom is provided with discharging opening 8, and charging aperture 9 is for the position of fermentation cabin 6, lateral partitions
4 are provided with some liquid-leadage holes, and fermentation cabin 6 connects sepage storage silo 7 by liquid-leadage hole, and sepage storage silo 7 is located under fermentation cabin 6
Side, is rotatablely equipped with two spiral conveying rollers 20 for being used to for material to be delivered to discharging surge bunker 5 by fermentation cabin 6 on feed bin 2, and two
Root spiral conveying roller 20 be arranged in parallel and is all connected with the first power set;It is rotatablely equipped with fermentation cabin 6 by the second power set
The agitating roller 21 of driving, agitating roller 21 include agitating shaft 211 and the stirring vane 212 being fixedly mounted on agitating shaft 211, spiral
The axis of the axis of conveying roller 20 and agitating roller 21 is vertically arranged, at least three groups of stirring vane 212, in two spiral conveying rollers 20
Between one group of stirring vane 212 is set, the both sides of two spiral conveying rollers 20 respectively set one group of stirring vane 212, agitating roller 21
Axially extending fluid flow paths 213 are provided with, agitating shaft 211 is arranged to hollow, and hollow cavity then forms liquid flow all
Road 213, fluid flow paths 213 connect hydrogen peroxide pumping line, and agitating roller 21 radially extends provided with some and connects liquid
The fluid hole 214 of circulation passage 213;The corresponding discharging surge bunker 5 in the top of feed bin 2 and the position of fermentation cabin 6 are provided with some waste gas outlets
10, each waste gas outlet 10 connects gas path pipe 114 by a bronchus, and gas path pipe 114 connects emission-control equipment 11,
Gas path pipe 114 is provided with vavuum pump 22;The bottom of sepage storage silo 7 is provided with sepage outlet 12, and sepage outlet 12 is connected at waste water
Device 13 is managed, wastewater treatment equipment 13 is mature equipment, be will not be repeated here;First power set, the second power set, vacuum
Pump 22 is all connected with control unit, and the first power set are preferably motor 19, and the second power set are preferably variable-frequency motor, control
Unit is preferably programmable controller.
Axially extending air ventilation passage 201 is equipped with every spiral conveying roller 20, air ventilation passage 201 connects
Oxygen pumping line, generally, oxygen pumping line are arranged on the end of spiral conveying roller 20, spiral conveying by swivel joint 23
Roller 20 is provided with some ventholes 202 for radially extending and connecting air ventilation passage 201, and venthole 202 includes setting gradually
Inlet end 2021, throughput 2022 and outlet side 2023, inlet end 2021 and outlet side 2023 are taper, throughput 2022
For tubular, the outside diameter of inlet end 2021 is more than the diameter of throughput 2022, and the outside diameter of outlet side 2023 is more than circulation
The small end of the diameter in portion 2022, inlet end 2021 and outlet side 2023 connects with throughput 2022.
The bottom of sepage storage silo 7 is provided with blow-back cleaning device, and blow-back cleaning device includes being installed on feed bin 2
And the air inlet pipe 18 of connection sepage storage silo 7, air inlet pipe 18 connect an air blower 16, air blower 16 passage time relay 15 connects
Control unit is connect, filter 17 is provided between air blower 16 and air inlet pipe 18, the high pressure for filtering the blowout of air blower 16 is empty
Gas.
For the ease of the temperature and oxygen concentration in control fermentation cabin 6, temperature sensor 24 and oxygen are installed in fermentation cabin 6
Gas concentration sensor 25, temperature sensor 24 and oxygen concentration sensor 25 are all connected with control unit.
Bronchus is provided with electric-control stop valve 14, and electric-control stop valve 14 connects control unit.
Emission-control equipment 11 includes exhaust gas treating tower 111, and the bottom of exhaust gas treating tower 111 is provided with Sewage outlet 113, gives up
The top of gas disposal tower 111 is provided with clean gas discharge 112, and the waste gas that the top of Sewage outlet 113 is provided with connection gas path pipe 114 enters
Gas port, the top of waste gas inlet are provided with spray deodoriser, are provided with above spray deodoriser close to the clean position of gas floss hole 112
Dry powder deodoriser, spray deodoriser includes the shower 116 of connection deodorant liquid pumping line 115, certainly, according to organic waste
Species is different, and those skilled in the art can voluntarily select suitable deodorant liquid.Shower 116 is along exhaust gas treating tower 111
Extend radially in exhaust gas treating tower 111, shower 116 is provided with some shower nozzles 117, and shower nozzle 117 can set multilayer, with
Reach optimal deodorizing effect;Dry powder deodoriser includes the housing 118 being arranged in exhaust gas treating tower 111, if housing 118 is provided with
Dry circuitous channel 119, the one end of circuitous channel 119 connection waste gas inlet, the other end connect clean gas floss hole 112, housing 118
Some suckings connected with circuitous channel 119 are provided with, deodorant powder is provided with housing 118, can according to the species of organic waste
To select different deodorant powder (deodorant liquid and deodorant powder are commercially available product, be will not be repeated here), gas path pipe
114 tilt and are installed on exhaust gas treating tower 111, and waste gas inlet is towards the bottom of exhaust gas treating tower 111, during spray, are unlikely to make
Obtain spray liquid to flow backward in gas path pipe 114, Sewage outlet 113 is connected with wastewater treatment equipment 13.
For composting device of the present invention, its course of work described below is more fully described.
Embodiment 1
It is 3 in mass ratio to take the municipal sludge that quality moisture content is 85% and the kitchen garbage that quality moisture content is 10%:1
Ratio be added to by charging aperture 9 in the fermentation cabin 6 of the composting device, close charging aperture 9, open electric-control stop valve 14, open
Dynamic vavuum pump 22 so that 15KPa negative pressure is formed in fermentation cabin 6, closes electric-control stop valve 14, starts variable-frequency motor and drives stirring
Roller 21 rotates, and is warming up to 45 DEG C, adds hydrogen peroxide, and its amount should make it that the quality moisture content of mixed material after stirring one day is 60%
It is 30 with C/N (mass ratio).By being processed as, temperature can reach more than 50 DEG C within second day, and maximum 70 was reached at the 3rd day
DEG C, then kept for two days at such a temperature, start motor 19, driven spiral conveying roller 20 to rotate, pass through spiral conveying roller 20
Rotation make sludge and solid organic castoff is transferred to discharging surge bunker 5, open discharging opening 8, discharge.Process is managed in this place
In, if oxygen concentration is less than certain value in fermentation cabin 6, such as oxygen volumetric concentration is less than 5%, then passes through spiral conveying roller 20
Supplemental oxygen, until the pressure in fermentation cabin 6 is higher than 20KPa, electric-control stop valve 14 is then opened, is vacuumized, waste gas is by top
Waste gas outlet 10 be expelled to emission-control equipment 11, the sewage in emission-control equipment 11 is then emitted into wastewater treatment equipment 13
In, focused on percolate.The processing unit only less than the 5 days compost treatments that can complete sludge and solid-state fluorescence material,
Processing time is substantially reduced, and exhaust-gas treatment is completely up to standard, and sewage, which also achieves, to be focused on, and saves resource.
It should be appreciated that the purposes of these embodiments is merely to illustrate the present invention and is not intended to the protection model of the limitation present invention
Enclose.In addition, it should also be understood that, after the technology contents of the present invention have been read, those skilled in the art can make each to the present invention
Kind change, modification and/or variation, all these equivalent form of values equally fall within the guarantor that the application appended claims are limited
Within the scope of shield.