CN203807351U - Breeding excrement biological drying system of livestock farm - Google Patents

Breeding excrement biological drying system of livestock farm Download PDF

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Publication number
CN203807351U
CN203807351U CN201420231683.7U CN201420231683U CN203807351U CN 203807351 U CN203807351 U CN 203807351U CN 201420231683 U CN201420231683 U CN 201420231683U CN 203807351 U CN203807351 U CN 203807351U
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biological dewatered
workshop
biological
ight soil
aeration
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梁富威
刘杭
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GUANGZHOU SHIPURUI ENVIRONMENTAL PROTECTION ENGINEERING Co Ltd
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GUANGZHOU SHIPURUI ENVIRONMENTAL PROTECTION ENGINEERING Co Ltd
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Abstract

The utility model discloses a breeding excrement biological drying system of a livestock farm. The system comprises a stirring system, a conveying system, an automatic dosing system, an aerating system, at least one biological drying workshop, an air draft system and a deodorization system. According to the system disclosed by the utility model, excrements in the livestock farm collected are mixed with auxiliary materials through the stirring system, and then, the mixed materials are transferred to the automatic dosing system at the top of the biological drying workshop through the conveying system, and the automatic dosing system automatically dispenses the materials to the biological drying workshop. In the biological drying workshop, heat generated by mixing the excrements and the auxiliary materials is transferred from bottom to top by the effect of the aerating system and the air draft system, so that the whole reactor material is uniform to heat and the temperature is raised, and therefore, the excrements are rapidly and biologically dried. Meanwhile, moisture in the materials is turned to water vapor which is discharged to the deodorization system under the effect of the air draft system to be purified and then discharged to air without secondary pollution.

Description

The biological dewatered system of plant's cultivation ight soil
Technical field
The utility model relates to the biological dewatered system of plant's cultivation ight soil.
Background technology
Effective improvement of pig farm pig manure, become a bottleneck of puzzlement pig industry development, become a primary pollution source of China's pollution of area source, with regard to its quantity discharged, it is industry and urban life waste discharge amount 10 times that its organism be take quantity discharged that COD is equivalent, in China's solid waste, all effectively processed now, the domestic refuse no matter useless dangerous thing of still endangering, and the ight soil on China pig farm is processed and is also rested in simple process or jejune technique.
The dejecta treatment method on pig farm mainly contains at present: burning method, desiccating method, deodorization process, resource utilization method (compost fermentation method).
Burning method, because containing organic substance in feces of livestock and poultry, adopts similar incineration treatment of garbage technology, makes its ashing, reach the object of decrement and kill harmful pathogenic agent, but can produce obnoxious flavour in treating processes, make many nutritive substances run off simultaneously, and big energy-consuming, investment is large, is therefore difficult for promoting;
Desiccating method is to utilize heat energy, sun power, wind energy homenergic, feces of livestock and poultry is processed, make feces of livestock and poultry remove within a certain period of time most of moisture, reach dry object, be not only to reduce the moisture in ight soil, but also to reach the effect of deodorizing and sterilizing, therefore, dried feces of livestock and poultry greatly reduces the pollution to environment, and dried feces of livestock and poultry can be processed into granulated fertilizer, or as the feeds of livestock and poultry, serve many purposes.According to the difference of thermal source and type of heating, desiccating method is divided into seasoning, high temperature and rapid drying, mechanical drying etc.Seasoning, current domestic being natural air drying or drying of taking, this method efficiency is low, and floor space is large, and cost of labor is high, and air is produced to secondary pollution, is not suitable for large-scale cultivationization cultivation factory; High temperature and rapid drying, at present domesticly adopts interior electrically heated or coal heat drying more, and this method need consume a large amount of energy, and tool investment is large, and the shortcomings such as processing cost height are not suitable for cultivating factory and promote; Mechanical drying method, domestic many employing screw extrusion are dry or filter press is dry, and this method need to consume a large amount of electric energy, needs to be equipped with powerful transformer; tool, cost of investment is high, and processing cost is high; the shortcomings such as maintenance cost is high, discharging water ratio high approximately 40%, are not suitable for large-scale cultivation factory and use.
Deodorization process, the taste gas that has of having identified feces of livestock and poultry generation at present mainly belongs to sulfocompound, nitrogenous compound, voltaile fatty acid and ketone etc.; It is generally acknowledged, ammonia, carbonic acid gas, methane and hydrogen sulfide are the major causes that causes atmospheric pollution and smell, take to add the medicament kill pathogens such as formalin, ethene, sodium bicarbonate, MB in feces of livestock and poultry, reduce the volatilization of ammonia, process after product and be used for the ruminant domestic animal of feeding, but chemical treatment method one-time investment is large, product cost is high, have secondary pollution situation to occur, be difficult to obtain good economic benefit, can not be smoothly for market be accepted.
Resource utilization method, the conventional recycling treatment process of pig farm ight soil is composting process at present, composting process has anaerobic composting, aerobic compost; Compost is a kind of resource reutilization technique; use conventional composting process, need to participate in a large amount of auxiliary material of mixing to regulate the water ratio of ight soil, and the compost fermentation time is more than 20 days; production cost is high; in addition, the fertilizer that make excrement composting produce has productivity effect, also needs the scale that reaches certain; will be by compost industrial scale; need the ight soil on each middle and small scale pig farm to being transported to same composting plant, the higher fresh pig dung of water ratio, in transportation, can produce secondary pollution.
Utility model content
The purpose of this utility model is to provide the biological dewatered system of a kind of plant's cultivation ight soil.
According to an aspect of the present utility model, a kind of plant cultivation ight soil quick biological drying system is provided, comprise stirring system, delivery system, automatic batching system, aerating system, at least one biological dewatered workshop, exhausting system and deodoration system.
Stirring system mixes ight soil and auxiliary material, and mixed material is delivered to delivery system.
Delivery system is delivered to above-mentioned mixed material the automatic batching system at top, biological dewatered workshop.
Automatic batching system is distributed to material in biological dewatered workshop automatically.
Aerating system is located at bottom, biological dewatered workshop, to bottom, biological dewatered workshop aeration.
Exhausting system is communicated with top, biological dewatered workshop, and the steam at top, biological dewatered workshop is evacuated in deodoration system.
Deodoration system drains in air after above-mentioned steam is purified.
In the utility model, plant's ight soil of collecting is mixed by stirring system and auxiliary material, then the material of mixing is transferred to the automatic batching system at top, biological dewatered workshop by delivery system, automatic batching system is distributed to material in biological dewatered workshop automatically, in biological dewatered workshop, by the effect of aerating system and exhausting system, ight soil and auxiliary material mix the heat producing and transmit from bottom to top, thereby make whole heap body material thermally equivalent, temperature raises, thereby make ight soil quick biological drying, moisture in material becomes water vapour simultaneously, water vapour purifies be discharged to deodoration system under the effect of exhausting system in, then be discharged in air, can not cause secondary pollution, in whole process, drying time is short, water content is low, production cost is low, simultaneously can high-temperature sterilization, effectively murder pathogenic bacteria, solve pig manure and deal with immunization issues and the ight soil transportation secondary pollution problem of generation improperly, and ight soil is good soil improvement agent after mummification, can be used for that processing and manufacturing is refining fertilizer, composite microbe fertilizer, biological organic fertilizer, organic-inorganic compound mixed fertilizer etc.
In some embodiments, the quantity in biological dewatered workshop can be four, four parallel arranging in biological dewatered workshop.Thus, four parallel mummification in biological dewatered workshop, can improve the treatment capacity of ight soil and raise the efficiency.
In some embodiments, automatic batching system can comprise rotary conveyor, eight motorized valves, four electric guard boards, two side shields, four level gages and control device, rotary conveyor is positioned at top, biological dewatered workshop, electric guard board is vertical on the feed track of rotary conveyor, the entrance of eight motorized valves is all communicated with the feed track of rotary conveyor, wherein four motorized valves are positioned at a side of rotary conveyor, and the outlet of four motorized valves lays respectively at top, four biological dewatered workshops, the location interval of above-mentioned four motorized valves and four electric guard boards is arranged, other four motorized valves are positioned at the opposite side of rotary conveyor, and the outlet of four motorized valves lays respectively at top, four biological dewatered workshops, two side shields are located at respectively the feed track both sides of rotary conveyor, four level gages are located at respectively in four biological dewatered workshops, height of materials signal in level gage detection of biological mummification workshop, and height of materials signal is sent to control device, control device receives material altitude signal, and transmit control signal to motorized valve and electric guard board.Thus, the height of materials detecting by level gage, control device eight motorized valves of control and four electric guard boards cooperatively interact and open and close, thereby make four biological dewatered workshop intermittent feedings, realize the automatization of charging.
In some embodiments, aerating system can comprise gas blower, aeration supervisor, a plurality of aeration branch pipe, perforation cover plate and haydite, the outlet of gas blower is communicated with aeration supervisor, aeration branch pipe is communicated with aeration supervisor, aeration supervisor is crisscross formula with a plurality of aeration branch pipes and arranges, and perforation cover plate is located on the ground in biological dewatered workshop, and aeration supervisor and aeration branch pipe are positioned at perforation cover plate below, solarization air cap is all arranged at the bottom of aeration branch pipe, and haydite is filled in around aeration branch pipe.Thus, the aeration supervisor that gas blower is arranged by crisscross formula and aeration branch pipe carry out aeration from bottom, biological dewatered workshop, make ight soil and auxiliary material mix the heat producing and make whole heap body material thermally equivalent from bottom to top, temperature raises, and solarization air cap is located at and is filled with haydite around the bottom of aeration supervisor and aeration branch pipe and aeration supervisor and aeration branch pipe and can makes aeration more even.
In some embodiments, aeration supervisor's below can be provided with U-shaped water shoot, and one end of U-shaped water shoot is positioned at aeration supervisor's below, and the other end is in communication with the outside.Thus, the waste water in biological dewatered workshop can be discharged from the U-shaped water shoot of bottom.
In some embodiments, delivery system can adopt worm conveyor.Thus, by worm conveyor convey materials, can realize automatization and control, without artificial transfer.
In some embodiments, exhausting system can adopt negative pressure centrifugal blower, and the entrance of negative pressure centrifugal blower is communicated with the top in four biological dewatered workshops, and the outlet of negative pressure centrifugal blower is communicated with deodoration system.Thus, by the negative pressure exhausting of negative pressure centrifugal blower, can make the water vapour of bank body top in biological dewatered workshop discharge outside workshop fast.
In some embodiments, deodorizing system can adopt biological deodorizing tower.Thus, water vapour is condensation in biological deodorizing system, and water vapour drains in the middle of air after biological deodorizing tower purifies, and does not cause secondary pollution.
Accompanying drawing explanation
Fig. 1 is the structural representation of the biological dewatered system of plant's cultivation ight soil of a kind of embodiment of the utility model;
Fig. 2 is that the biological dewatered system of plant's cultivation ight soil shown in Fig. 1 is along the structural representation of A direction;
Fig. 3 is the local enlarged diagram at the plant's cultivation biological dewatered system B of the ight soil place shown in Fig. 2;
Fig. 4 is the location diagram in aerating system and biological dewatered workshop in the biological dewatered system of plant shown in Fig. 2 cultivation ight soil;
Fig. 5 is the syndeton schematic diagram of aeration supervisor, a plurality of aeration branch pipes in the biological dewatered system of plant's cultivation ight soil shown in Fig. 2;
Fig. 6 is that the biological dewatered system of plant's cultivation ight soil shown in Fig. 5 is along the structural representation of C-C direction;
Fig. 7 is that the biological dewatered system of plant's cultivation ight soil shown in Fig. 5 is along the structural representation of D-D direction;
Fig. 8 is the schema that the plant's biological dewatered system of cultivation ight soil shown in Fig. 1 is carried out ight soil mummification.
Embodiment
Below in conjunction with accompanying drawing, the utility model is described in more detail.
Fig. 1 to Fig. 7 has schematically shown the structure of the biological dewatered system of plant's cultivation ight soil of a kind of embodiment of the utility model.
As shown in Figures 1 to 7, the biological dewatered system of plant's cultivation ight soil, comprises stirring system 1, delivery system 2, automatic batching system 3, aerating system 4, biological dewatered workshop 5, exhausting system 6 and deodoration system 7.
As shown in Figure 1, stirring system 1 evenly mixes cultivation ight soil and the auxiliary material collected, and by mixed mass transport to delivery system 2.
In the present embodiment, stirring system 1 employing stirrer realization, guarantees to cultivate ight soil and auxiliary material mixes.In other embodiments, stirring system 1 also can be realized by hand mixing, as long as cultivation ight soil and auxiliary material mix.
In the present embodiment, auxiliary material adopts ferment, after ight soil and ferment mix, because endogenous reaction can produce a large amount of heats.
As shown in Figure 1, the material that delivery system 2 transports stirring system 1 is delivered in the automatic batching system 3 at 5 tops, biological dewatered workshop.
In this enforcement, delivery system 2 adopts worm conveyor, and the material after stirrer 1 stirs is delivered to the automatic batching system 3 that is arranged in 5 tops, biological dewatered workshop by worm conveyor, realizes automatization and controls, and without artificial transfer, raises the efficiency.
As shown in Figure 1 and Figure 2, in the present embodiment, the quantity in biological dewatered workshop 5 is four, four parallel arranging in biological dewatered workshop 5, and four parallel mummification in biological dewatered workshop 5, can improve the treatment capacity of ight soil and raise the efficiency.In other embodiments, the quantity in biological dewatered workshop 5 can change according to ight soil treatment capacity, increases or reduces.
As shown in Figure 1, automatic batching system 3 is positioned at 5 tops, four biological dewatered workshops.
As shown in Figures 2 and 3, automatic batching system 3 comprises rotary conveyor 31, eight motorized valves 32, four electric guard boards 33, two side shields 34, four level gages 35 and control device 36.
Control device 36 is electrically connected to motorized valve 32, to motorized valve 32, sends open/close control signal.
Control device 36 is electrically connected to electric guard board 33, to electric guard board 33, sends the control signal that falls/rise.
In the present embodiment, control device 36 is microprogram control units.In other embodiments, control device 36 can be also Combinational Logic Control device, can also be cpu controller etc.
As shown in Figure 1, rotary conveyor 31 is positioned at the top in four biological dewatered workshops 5, and rotary conveyor 31 is convey materials from left to right.
As shown in Figures 2 and 3, two side shields 34 are separately fixed at the feed track both sides of rotary conveyor 31, guarantee that the material on rotary conveyor 31 does not drop.
As shown in Figures 2 and 3, four electric guard boards 33 are vertically mounted on the feed track of rotary conveyor 31 successively, four electric guard boards 33 are under the control of control device 36, can from the feed track of rotary conveyor 31, lift or drop on the feed track of rotary conveyor 31, realize blocking-up and the clearance of material.
As shown in Figures 2 and 3, the lower end entrance that is positioned at four motorized valves 32 of rotary conveyor 31 feed track upsides is communicated with the feed track of rotary conveyor 31, the upper end outlet of four motorized valves 32 lays respectively at the top in four biological dewatered workshops 5, and the material on rotary conveyor 31 feed tracks can drop in biological dewatered workshop 5 by motorized valve 32.
As shown in Figures 2 and 3, the upper end entrance that is positioned at four motorized valves 32 of rotary conveyor 31 feed track downsides is communicated with the feed track of rotary conveyor 31, the lower end outlet of four motorized valves 32 lays respectively at the top in four biological dewatered workshops 5, and the material on rotary conveyor 31 feed tracks can drop in biological dewatered workshop 5 by motorized valve 32.
As shown in Figure 2, four motorized valves 32 that are positioned at rotary conveyor 31 feed track upsides are symmetrical about rotary conveyor 31 feed tracks with four motorized valves 32 that are positioned at rotary conveyor 31 feed track downsides, and the outlet of two motorized valves 32 is arranged at the top in each biological dewatered workshop 5.
As shown in Figure 3, the material on rotary conveyor 31 feed tracks can drop to by two motorized valves 32 that are arranged symmetrically with up and down (K direction as shown in Figure 3 and J direction) in biological dewatered workshop 5.
As shown in Figure 2, being positioned at four motorized valves 32 of rotary conveyor 31 feed track upsides and the location interval of four electric guard boards 33 arranges, an electric guard board 33 is arranged on each motorized valve 32 right side, when electric guard board 33 drops on the feed track of rotary conveyor 31, the material in electric guard board 33 left sides can drop in biological dewatered workshop 5 by two motorized valves 32 in electric guard board 33 left sides.
Four level gages 35 are electrically connected to control device 36.
As shown in Figure 1, four level gages 35 are arranged on respectively in four biological dewatered workshops 5, height of materials signal in level gage 35 detection of biological mummification workshops 5, and height of materials signal is sent to control device 36, control device 36 receives material altitude signal, and sends corresponding control signal to motorized valve 32 and electric guard board 33.
As depicted in figs. 1 and 2, the height of materials signal that from left to right level gage 35 in first biological dewatered workshop 5 detects is during lower than set(ting)value, first electric guard board 33 that control device 36 is controlled from left to right drops on the feed track of rotary conveyor 31, and two motorized valves 32 of controlling first 5 tops, biological dewatered workshop are opened, now, the material on rotary conveyor 31 falls into first biological dewatered workshop 5 automatically; When the height of materials signal that the level gage 35 in first biological dewatered workshop 5 detects reaches set(ting)value, first electric guard board 33 that control device 36 is controlled from left to right lifts from the feed track of rotary conveyor 31, and two motorized valves 32 controlling first 5 tops, biological dewatered workshop cut out, now, first biological dewatered workshop 5 chargings are complete.From left to right second biological dewatered workshop 5, the 3rd biological dewatered workshop 5 are identical with the feeding manner in above-mentioned first biological dewatered workshop 5 with the feeding manner in the 4th biological dewatered workshop 5, it is the height of materials signal that control device 36 detects by receiving four level gages 35, then control eight motorized valve 32 On/Off, and control four electric guard boards 33 and lift/fall, thereby realize the intermittency check of charging in four biological dewatered workshops 5.
In the present embodiment, the quantity of motorized valve 32 is eight, and the quantity of electric guard board 33 is four.In other embodiments, the quantity of motorized valve 32, electric guard board 33 changes according to the quantity in biological dewatered workshop 5, the quantity of motorized valve 32 is the twice of biological dewatered workshop 5 quantity, there are two motorized valves 32 top of guaranteeing each biological dewatered workshop 5, and the quantity of electric guard board 33 is identical with biological dewatered workshop 5 quantity.
Automatic batching system 3 is distributed to material in each biological dewatered workshop 5 automatically, realizes automated operation, raises the efficiency.
As shown in Figures 4 to 7, aerating system 4 comprises gas blower 41, aeration supervisor 42, a plurality of aeration branch pipe 43, perforation cover plate 44 and haydite 45.
The outlet of gas blower 41 is communicated with aeration supervisor 42.
As shown in Figure 5, in the present embodiment, in each biological dewatered workshop 5, the quantity of aeration branch pipe 43 is six.In other embodiments, the quantity of aeration branch pipe 43 can change as required.
As shown in Figure 4 and Figure 5, aeration branch pipe 43 and aeration supervisor 42 is communicated with, and in each biological dewatered workshop 5, aeration is responsible for 42 and six aeration branch pipes 43 and is crisscross formula and arranges.
As shown in Figure 6, the bottom of aeration branch pipe 43 forms solarization air cap 46, and the air-flow that gas blower 41 bloats exposes by solarization air cap 46.
As shown in Figure 6, in the present embodiment, the outgassing direction of solarization air cap 46 and horizontal plane direction are in angle of 45 degrees.In other embodiments, the angle of the outgassing direction of solarization air cap 46 and horizontal plane direction can change according to actual needs.
As shown in Figure 6 and Figure 7, on each 5 ground, biological dewatered workshop, be equipped with piercing cap plate 44, aeration supervisor 42 and aeration branch pipe 43 are embedded in perforation cover plate 44 belows, and haydite 45 is filled in around aeration branch pipe 43.Aeration supervisor 42 and aeration branch pipe 43 that gas blower 41 is arranged by crisscross formula carry out aeration from 5 bottoms, biological dewatered workshop, make ight soil and auxiliary material mix the heat producing and make whole heap body material thermally equivalent from bottom to top, temperature raises, can be elevated to 80 degree, aeration branch pipe 43 is filled with haydite 45 around can make aeration more even.
As shown in Figure 7, one end of U-shaped water shoot 47 is positioned at aeration supervisor 42 below, and the other end is in communication with the outside, and the waste water in biological dewatered workshop 5 can be discharged from the U-shaped water shoot 47 of bottom.
In the present embodiment, exhausting system 6 adopts negative pressure centrifugal blower.In other embodiments, exhausting system 6 also can adopt pipeline vacuum fan.
The exhausting entrance of negative pressure centrifugal blower is communicated with the top in four biological dewatered workshops 5, and the outlet of negative pressure centrifugal blower is communicated with deodoration system 7, thereby the steam producing in biological dewatered workshop 5 is evacuated in deodoration system 7.
By the effect of aerating system 4 and exhausting system 6, the heat that in biological dewatered workshop 5, ight soil and auxiliary material mixing produce makes whole heap body material thermally equivalent from bottom to top, temperature raises, thereby make ight soil quick biological drying, moisture in material becomes water vapour simultaneously, and water vapour is discharged in deodoration system 7 under the effect of exhausting system 6.
As shown in Figure 1, in the present embodiment, deodoration system 7 adopts biological deodorizing tower, water vapour condensation in biological deodorizing tower, and water vapour drains in the middle of air after biological deodorizing tower purifies, and does not cause secondary pollution.In other embodiments, deodoration system 7 also can adopt the deodoration systems such as gac.
Plant's ight soil of collecting is mixed by stirring system 1 and auxiliary material, then the material of mixing is transferred to the automatic batching system 3 at 5 tops, biological dewatered workshop by delivery system 2, automatic batching system 3 is distributed to material in biological dewatered workshop 5 automatically, in biological dewatered workshop 5, by the effect of aerating system 4 and exhausting system 6, ight soil and auxiliary material mix the heat producing and transmit from bottom to top, thereby make whole heap body material thermally equivalent, temperature raises, thereby make ight soil quick biological drying, moisture in material becomes water vapour simultaneously, water vapour is discharged in deodoration system 7 and purifies under the effect of exhausting system 6, then be discharged in air, can not cause secondary pollution, in whole process, drying time is short, water content is low, production cost is low, simultaneously can high-temperature sterilization, effectively murder pathogenic bacteria, solve pig manure and deal with immunization issues and the ight soil transportation secondary pollution problem of generation improperly, and ight soil is good soil improvement agent after mummification, can be used for that processing and manufacturing is refining fertilizer, composite microbe fertilizer, biological organic fertilizer, organic-inorganic compound mixed fertilizer etc.
Fig. 8 has schematically shown the flow process that the plant's biological dewatered system of cultivation ight soil shown in Fig. 1 is carried out ight soil mummification.
As shown in Figure 8, to carry out the flow process of ight soil mummification as follows for the biological dewatered system of plant cultivation ight soil:
Step 101: the cultivation ight soil that is 60%~85% by water ratio is collected to do clear excrement form;
Step 102: the ight soil of collecting and ferment are mixed by stirring system 1;
Step 103: the mixed material of step 102 gained is delivered to 5 tops, biological dewatered workshop by delivery system 2;
Step 104: the material at 5 tops, biological dewatered workshop is gone in biological dewatered workshop 5 by automatic batching system 3;
Step 105: carry out aeration in 5 bottoms, biological dewatered workshop by aerating system 4, the heat of auxiliary material and the endogenous reaction generation of material is transmitted from bottom to top, thereby make whole heap body thermally equivalent;
Step 106: carry out exhausting at 5 tops, biological dewatered workshop by exhausting system 6, biological dewatered workshop 5 is under the acting in conjunction of bottom forced ventilation and top exhausting, and the moisture content in material becomes water vapour to the evaporation of heap body top;
Step 107: the water vapour of piling body top in step 106 is evacuated in deodoration system 7 and purifies by exhausting system 6, then drains in the middle of air;
Step 108: material is in the endogenous heat production of the interior continuous process in biological dewatered workshop 5, forced ventilation, and the circulating treatment procedure of exhausting, after too much day processing, moisture content reaches the standard of mummification, and after 7 days process, the water ratio of material can be less than 30%.
Above-described is only embodiments more of the present utility model.For the person of ordinary skill of the art, not departing under the prerequisite of the utility model creation design, can also make some distortion and improvement, these all belong to protection domain of the present utility model.

Claims (8)

1. plant cultivates the biological dewatered system of ight soil, it is characterized in that, comprise stirring system (1), delivery system (2), automatic batching system (3), aerating system (4), at least one biological dewatered workshop (5), exhausting system (6) and deodoration system (7)
Described stirring system (1) mixes ight soil and auxiliary material, and mixed material is delivered to delivery system (2),
Described delivery system (2) is delivered to above-mentioned mixed material the automatic batching system (3) at top, biological dewatered workshop (5),
Described automatic batching system (3) is distributed to material in biological dewatered workshop (5) automatically,
Described aerating system (4) is located at bottom, biological dewatered workshop (5), to biological dewatered workshop (5) bottom aeration,
Described exhausting system (6) is communicated with top, biological dewatered workshop (5), the steam at top, biological dewatered workshop (5) is evacuated in deodoration system (7),
Described deodoration system (7) drains in air after above-mentioned steam is purified.
2. the biological dewatered system of plant's cultivation ight soil according to claim 1, is characterized in that, the quantity in described biological dewatered workshop (5) is four, and four biological dewatered workshops (5) are parallel arranges.
3. plant according to claim 2 cultivates the biological dewatered system of ight soil, it is characterized in that, described automatic batching system (3) comprises rotary conveyor (31), eight motorized valves (32), four electric guard boards (33), two side shields (34), four level gages (35) and control device (36), described rotary conveyor (31) is positioned at top, biological dewatered workshop (5), electric guard board (33) is vertical on the feed track of rotary conveyor (31), the entrance of eight motorized valves (32) is all communicated with the feed track of rotary conveyor (31), wherein four motorized valves (32) are positioned at a side of rotary conveyor (31), and the outlet of four motorized valves (32) lays respectively at top, four biological dewatered workshops (5), above-mentioned four motorized valves (32) are arranged with the location interval of four electric guard boards (33), other four motorized valves (32) are positioned at the opposite side of rotary conveyor (31), and the outlet of four motorized valves (32) lays respectively at top, four biological dewatered workshops (5), two described side shields (34) are located at respectively the feed track both sides of rotary conveyor (31), four level gages (35) are located at respectively in four biological dewatered workshops (5), height of materials signal in level gage (35) detection of biological mummification workshop (5), and height of materials signal is sent to control device (36), control device (36) receives material altitude signal, and transmit control signal to motorized valve (32) and electric guard board (33).
4. plant according to claim 3 cultivates the biological dewatered system of ight soil, it is characterized in that, described aerating system (4) comprises gas blower (41), aeration supervisor (42), a plurality of aeration branch pipes (43), perforation cover plate (44) and haydite (45), the outlet of described gas blower (41) is communicated with aeration supervisor (42), aeration branch pipe (43) is communicated with aeration supervisor (42), described aeration supervisor (42) is crisscross formula with a plurality of aeration branch pipes (43) and arranges, described perforation cover plate (44) is located on ground, biological dewatered workshop (5), aeration supervisor (42) and aeration branch pipe (43) are positioned at perforation cover plate (44) below, the bottom of aeration branch pipe (43) is provided with solarization air cap (46), described haydite (45) is filled in aeration branch pipe (43) around.
5. plant according to claim 4 cultivates the biological dewatered system of ight soil, it is characterized in that, described aeration supervisor's (42) below is provided with U-shaped water shoot (47), one end of described U-shaped water shoot (47) is positioned at aeration supervisor's (42) below, and the other end is in communication with the outside.
6. according to the biological dewatered system of plant's cultivation ight soil described in any one in claim 2~5, it is characterized in that, described delivery system (2) adopts worm conveyor.
7. plant according to claim 6 cultivates the biological dewatered system of ight soil, it is characterized in that, described exhausting system (6) adopts negative pressure centrifugal blower, the entrance of negative pressure centrifugal blower is communicated with the top in four biological dewatered workshops (5), and the outlet of negative pressure centrifugal blower is communicated with deodoration system (7).
8. the biological dewatered system of plant's cultivation ight soil according to claim 7, is characterized in that, described deodoration system (7) adopts biological deodorizing tower.
CN201420231683.7U 2014-04-29 2014-05-07 Breeding excrement biological drying system of livestock farm Active CN203807351U (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103922816A (en) * 2014-04-29 2014-07-16 广州市施普瑞环保工程有限公司 Bio-drying system and method for excrement in livestock farm

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103922816A (en) * 2014-04-29 2014-07-16 广州市施普瑞环保工程有限公司 Bio-drying system and method for excrement in livestock farm
CN103922816B (en) * 2014-04-29 2016-03-23 广州市施普瑞环保工程有限公司 The biological dewatered system and method for plant's cultivation ight soil

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