CN206502752U - A kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics - Google Patents
A kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics Download PDFInfo
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- CN206502752U CN206502752U CN201621490938.7U CN201621490938U CN206502752U CN 206502752 U CN206502752 U CN 206502752U CN 201621490938 U CN201621490938 U CN 201621490938U CN 206502752 U CN206502752 U CN 206502752U
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
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- 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
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Abstract
The utility model discloses a kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics, including:Water-bath;Temperature measuring equipment is provided with the anaerobic fermentation tank being placed in the water-bath, the anaerobic fermentation tank;And the gas collecting apparatus being connected with the anaerobic fermentation tank exhaust outlet.The problem of the utility model solves the antibiotic environmental pollution, difficult degradation, low resource utilization of the organic solid castoff Treatment and recovery such as current feces of livestock and poultry technology presence.
Description
Technical field
The utility model belongs to that bazardous waste is innoxious and recycling field, and in particular to a kind of degradable livestock and poultry
The anaerobic composting device of antibiotic in excrement.
Background technology
Antibiotic be the microorganisms such as fungi, actinomyces or bacterium produced in its metabolic process have kill or suppress it
One class chemical substance of his microbial action.Ratify antibiotic first from 1950s FDA to use
Make after feed addictive, feeding antibiotic consumption is increased rapidly in the world.China is antibiotic life maximum in the world
Produce one of state and country of consumption, it is estimated that, the usage amount of the current annual antibiotic of China reaches 210,000 tons, ranks the first in the world, its
In there are about 46.1% be used for livestock and poultry breeding industry, equivalent to 4 times of U.S.'s poultry industry usage amount in 1999.
At present, the excrement that annual livestock and poultry give off is up to industrial solid solid waste mostly 2,500,000,000 tons more than twice.Zhang Shu
Clearly, the research such as Halling-Sorensen, Gulknwska shows that animal is used after antibiotic, only absorbs profit by animal on a small quantity
With thering is 25%~75% or even 70%~90% to be excreted through alimentary canal with feces of livestock and poultry, urine.A part is with breeding wastewater
Into sewage plant, and antibiotic is not high in the clearance of sewage treatment plant, causes a large amount of antibiotic to pass through leaching, rainwash
Etc. surface water and groundwater is entered, various murders by poisoning are caused to aquatile, causes river antibiotic pollution, threatens mankind's drinking water
Safety;Another part as organic fertilizer apply farmland, cause soil antibiotic pollute, destroy edaphon structure of community and
Function, and transmitted to crops uptake and accumulation, and by food chain, the normal activities of influence plant, animal and microorganism,
The health of the final threat mankind.A large amount of antibiotic, which enter in environment, can also induce pathogen drug resistance, cause drug resistance pathogenic bacteria
Generation and diffusion, thus caused environmental pollution and eco-toxicity have been increasingly becoming a society of people's common concern and asked
Topic.Therefore we will have a profound understanding of the harm of abuse of antibiotics, be necessary to take measures to remove before feces of livestock and poultry utilization
Antibiotic residue therein, to reach the double shield of economic benefit and safety and Health.
Include China in countries in the world, feces of livestock and poultry is used in farmland frequently as organic fertilizer, although feces of livestock and poultry can give agriculture
Crop provides various nutriments, improves soil quality, but their soil application improves the risk of water and soil pollution, they
Pathogen and unstable material may be contained, such as organic nitrogen, titanium pigment and various antibiotic residues are in feces of livestock and poultry.
The antibiotic that the research such as Rynk, Kuchta shows to work as in feces of livestock and poultry, which enters in soil or lake, metastable to have 5-9
Individual month.Antibiotic long-term existence brings huge potential risk in environment to the public and environmental health.
Composting process is common dung recovery, innoxious means, is at home and abroad widely studied and answers for a long time
With.Focused mostly in recent years in antibiotic research is removed to livestock excrement composting in sulfamido, and it is fresh to tetracycline antibiotics
Have been reported that, especially degraded of the anaerobic composting to tetracycline antibiotics in feces of livestock and poultry only has fragmentary research.
Anaerobic composting method is one of main processing ways of feces of livestock and poultry, can effectively pollution abatement by anaerobic digestion
Substance environment load, and reclaim available biomass energy.Therefore, during anaerobic composting, livestock excrement composting mistake is verified
The main-control factors and key parameter of journey tetracycline antibiotics conversion degraded, for the ecological wind of exploitation animal waste antibiotic
Cut control technology and technical basis is provided in danger.
Utility model content
In order to overcome the antibiotic environment that the organic solid castoff Treatment and recovery such as current feces of livestock and poultry technology is present
The problem of pollution, difficult degradation, low resource utilization, the technical problems to be solved in the utility model is to provide a kind of capable of being fast degraded
The anaerobic composting device of tetracycline antibiotics in feces of livestock and poultry.
A kind of anaerobic composting device of use for laboratory fast degradation feces of livestock and poultry tetracycline antibiotics, including:
Water-bath;
Temperature measuring equipment is provided with the anaerobic fermentation tank being placed in the water-bath, the anaerobic fermentation tank;
And the gas collecting apparatus being connected with the exhaust outlet of the anaerobic fermentation tank.The utility model device is used for animal dung
Just anaerobic composting processing is carried out, key is to control in compost center temperature, fast degradation feces of livestock and poultry by water-bath
Tetracycline antibiotics.
Preferably, the anaerobic fermentation tank includes tank body, cover, the ring-type being distributed in the tank body at different height modeling
Charging tray piece, the sample tap on the tank wall and the injection port and exhaust outlet being opened on the cover.
Further, tank body and cover are connected by flange buckle, are easy to the arrangement to fermentation tank;The injection port and sampling
Mouth is also respectively equipped with the appropriately sized closure connected by flange buckle;The discharge outlet is connected with drainpipe, and drainpipe draws
Go out in the hopper to outside water-bath.
Further, the sample tap is located on the side wall of body lower half.
Water-bath filled water in pan can adjust temperature to optimal graduation mark according to actual requirement, and windrow is maintained by water-bath
The temperature at center is 25 DEG C~70 DEG C, monitors the temperature of compost center in fermentation tank in composting process by temperature measuring equipment,
It is further preferred that the ring-shaped plastics disc is fixed in the tank body by support frame, and each ring-type modeling
Artificial cellosilk is wound on charging tray piece.Ring-shaped plastics disc is added to be wrapped on the bond area of microbial cells, disc
Artificial cellosilk contributes to the attachment and breeding of microbial cells.
It is further preferred that the center of the tank body is provided with vertically arranged filter core, the filter core is by inside and outside two sleeves
It is arranged and forms, draining micropore is offered on the barrel of outer sleeve, inner sleeve is close to outer sleeve setting and the bottom of inner sleeve is abutted
The discharge outlet.
It is further preferred that the top of the inner sleeve protrudes from the top of outer sleeve.
It is further preferred that provided with the through hole with inner sleeve match of pipe diameter on the cover and with inner sleeve corresponding position,
The through hole carries closure.Through hole sets convenient extraction inner sleeve.
Filter core is used for adjusting the moisture content of windrow, when moisture content is higher than required windrow moisture content, opens the sealing of through hole
Lid, inner sleeve is extracted, and windrow reclaimed water lease making osmosis is entered in outer sleeve by Small circular aperture, and water is arranged by drainpipe
Go out to enter hopper;When windrow moisture content needed for moisture content meets, inner sleeve is inserted into outer sleeve, stops draining.
Temperature measuring equipment is used for the temperature that windrow center is monitored in composting process, can use direct reading thermometer,
By temperature reading adjust water-bath in heating-up temperature, for improve automaticity, also can using temperature sensor with it is right
In the controller answered, the utility model preferably, the temperature measuring equipment is temperature sensor, and the thermometric of the temperature sensor is visited
Set in the middle part of head is located in tank body and close to filter core;;Further, controller is additionally provided with, the temperature sensor accesses the control
Device processed, the temperature-controlled portion of the water-bath accesses and is controlled by the controller.
The controller sheet is as conventional controller, such as PLC or other data processing equipments, temperature sensor
Windrow center temperature is measured, when temperature is less than design temperature, at temperature sensor transmission signal to PLC or data
Device, PLC or data processing equipment control water-bath heating are managed, when windrow central point temperature is higher than design temperature,
Temperature sensor, which transmits signal to PLC or data processor PLC or data processor controlled water-bath, to be stopped
Heating, the change procedure of the temperature of feces of livestock and poultry is the important indicator whether compost becomes thoroughly decomposed.
Gas collecting apparatus is connected with fermentation tank by airway tube, and airway tube uses PVC sebific ducts, with certain corrosion resistance
Energy, high temperature resistant, steady performance.
In the utility model, preferably by draining water gathering of gas law, the gas collecting apparatus includes a gas bottle and a collection
Saturated aqueous common salt is contained in tank, the gas bottle, the outlet of airway tube is located in gas bottle and close to bottle mouth position, a draining
Pipe one end insertion gas bottle top, the other end are connected in the water leg.Biogas is produced in one side fermentation flask and enters gas collection
Bottle, reaches in saturated common salt hydraulic pressure people's collection bottle after certain volume, biogas is collected by draining water gathering of gas law;On the other hand prevent
Air enters fermentation flask, reaches anaerobic state.
Device of the present utility model shortens the compost time, carries out anaerobic composting using the utility model device, 15 days i.e.
It can complete, the compost time of prior art is generally 20~35 days, and the utility model apparatus structure is simple, facilitates feasible.
Brief description of the drawings
Fig. 1 is the anaerobic composting structure drawing of device of tetracycline antibiotics in feces of livestock and poultry capable of being fast degraded.
Fig. 2 is the utility model fermentation tank structural representation.
Label reference in Fig. 1:1 water-bath, 2 hoppers, 3 anaerobic fermentation tanks, 4 feces of livestock and poultry, 21 controllers, 22 lead
Tracheae, 23 gas bottles, 24 saturated aqueous common salts, 25 separation cases, 26 water legs;
Reference in Fig. 2:5 covers, 6 injection ports, 7 flange buckles, 8 ring-shaped plastics discs, 9 support frames, 10 staple fibres
Silk, 11 micropores, 12 temperature sensors, 13 exhaust outlets, 14 filter cores, 15 inner sleeves, 16 temperature probes, 17 outer sleeves, 18 sample taps,
19 support feets, 20 drainpipes, 27 through holes.
Embodiment
As depicted in figs. 1 and 2, in a kind of degradable feces of livestock and poultry tetracycline antibiotics anaerobic composting device such as Fig. 1
With shown in Fig. 2, a kind of anaerobic composting device, including water-bath 1, anaerobic fermentation tank 3 and gas collecting apparatus, water-bath can be using experiment
Often use water-bath in room.
The structural representation of anaerobic fermentation tank as shown in Fig. 2 including tank body and cover 5, supported by support feet 19, tank body and
Connected between cover by flange buckle 7, side opens up exhaust outlet 13, opposite side and opened up and passes through at injection port 6, injection port on cover
Corresponding flange buckle connects closure.A sample tap 18 is opened up on the lower half side wall of tank body, sample tap passes through corresponding method
Orchid button connection closure, tank base opens up discharge outlet, and discharge outlet connection drainpipe 20, drainpipe 20 is connected to outside water-bath
Hopper 2 in.
If installing dried layer ring-shaped plastics disc 8 by support frame 9 in tank body, ring-shaped plastics disc be fixed on support frame and
At different height in tank body, 2~8 layers are traditionally arranged to be, sets and is wound with 5 layers, ring-shaped plastics disc in present embodiment
Artificial cellosilk 10, and artificial cellosilk also can be wound in network structure on ring-shaped plastics disc.
Anaerobic fermentation tank is interior and (i.e. filter core fills vinyl disc from all rings positioned at the vertically arranged filter core 14 in tank body center
The center of piece is passed through), filter core is made up of inner sleeve 15 and outer sleeve 17, and some micropores 11, inner sleeve are uniformly opened up on outer sleeve
Cylinder inserts in outer sleeve and is close to outer sleeve setting, and inner sleeve pipe wall not perforate, the bottom of inner sleeve abuts the row of tank base
The mouth of a river, top are higher than on outer sleeve, cover 5 opens up through hole 27, the aperture of through hole and the caliber of inner sleeve with inner sleeve corresponding position
Match, inner sleeve is extracted during moisture content out for adjusting, through hole carries closure.
Using temperature sensor 12 and controller 21 as temperature regulating device in present embodiment, the thermometric of temperature sensor is visited
First 16 located at the interior middle part of tank body, and is set against filter core, and temperature sensor is connected to the controller 21 outside fermentation tank by wire,
Controller is that the temperature control part in conventional controller, water-bath is accessed and is controlled by the controller, and controller receives temperature
The temperature information of sensor, the water temperature in water-bath is controlled by the temperature information received, and then control windrow in fermentation tank
The temperature of center.
Feces of livestock and poultry 4 is placed in anaerobic fermentation tank, and the biogas produced in fermentation process is collected using draining water gathering of gas law, including
One gas bottle 23, gas bottle is placed in the separation case 25 being arranged side by side with water-bath, and saturated aqueous common salt 24 is contained in gas bottle,
The one end of airway tube 22 is connected with the exhaust outlet of fermentation tank, other end insertion gas bottle is interior and close bottle mouth position, a drainpipe one
In water leg 26 outside end insertion gas bottle bottom, other end access separation case.
The technical process for carrying out feces of livestock and poultry anaerobic composting by said apparatus is as follows:
(1) feces of livestock and poultry is well mixed with the conditioner through grinding, obtains mixing windrow;
(2) in the laying of fermentation flask bottom one layer of sand, activated carbon granule, (activated carbon and sandstone can be by quality 1:1 mixture).
(3) mixing windrow is placed in fermentation flask, carries out lucifuge anaerobic fermentation.
(4) mixing windrow is placed in fermentation tank, then fermentation tank is positioned on water-bath, is connected gas collecting apparatus, is sent out
Ferment.
(5) temperature in fermentation tank is controlled to be 25 DEG C~70 DEG C by water-bath in anaerobic fermentation process.
(6) in composting process, a sample was taken every 2 days, compost terminated compost to 15 days.
(7) tetracycline antibiotics content detection is carried out to the sample taken, and to pH value, moisture content, biodegradability
BDM is measured, and observes its dynamic change.
Embodiment above is only preferred embodiment of the present utility model, is further detailed to the utility model
Describe in detail bright, be illustrative.The utility model is simultaneously not restricted to the described embodiments, and is not departing from the utility model spirit and model
On the premise of enclosing, the utility model can have various variations and improvement.Therefore, it is all according to present utility model application scope done it is any
Change modification, is belonged within protection domain of the present utility model.
Claims (8)
1. a kind of anaerobic composting device of use for laboratory fast degradation feces of livestock and poultry tetracycline antibiotics, it is characterised in that bag
Include:
Water-bath;
Temperature measuring equipment is provided with the anaerobic fermentation tank being placed in the water-bath, the anaerobic fermentation tank;
And the gas collecting apparatus being connected with the exhaust outlet of the anaerobic fermentation tank.
2. anaerobic composting device according to claim 1, it is characterised in that the anaerobic fermentation tank include tank body, cover, point
It is distributed in the tank body ring-shaped plastics disc at different height, the sample tap on the tank wall and is opened in institute
State the injection port and exhaust outlet on cover.
3. anaerobic composting device according to claim 2, it is characterised in that the ring-shaped plastics disc is fixed by support frame
Artificial cellosilk is wound in the tank body, and on each ring-shaped plastics disc.
4. anaerobic composting device according to claim 2, it is characterised in that the center of the tank body is provided with vertically arranged filter
Core, the filter core is arranged by inside and outside two sleeves and formed, and draining micropore is offered on the barrel of outer sleeve, inner sleeve is close to overcoat
Cylinder is set and the bottom of inner sleeve abuts the discharge outlet.
5. anaerobic composting device according to claim 4, it is characterised in that the top of the inner sleeve protrudes from outer sleeve
Top.
6. anaerobic composting device according to claim 5, it is characterised in that be provided with the cover and with inner sleeve corresponding position
With the through hole of inner sleeve match of pipe diameter, the through hole carries closure.
7. anaerobic composting device according to claim 4, it is characterised in that the temperature measuring equipment is temperature sensor, described
The temperature probe of temperature sensor is located at middle part and close filter core setting in tank body.
8. anaerobic composting device according to claim 7, it is characterised in that be additionally provided with controller, the temperature sensor connects
Enter the controller, the temperature-controlled portion of the water-bath accesses and is controlled by the controller.
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CN201621490938.7U CN206502752U (en) | 2016-12-30 | 2016-12-30 | A kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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CN108911801A (en) * | 2018-08-28 | 2018-11-30 | 倪晓燕 | A kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics |
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CN108911801A (en) * | 2018-08-28 | 2018-11-30 | 倪晓燕 | A kind of anaerobic composting device of fast degradation feces of livestock and poultry tetracycline antibiotics |
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CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170919 Termination date: 20201230 |
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CF01 | Termination of patent right due to non-payment of annual fee |