CN108059497A - A kind of municipal sludge compositing system and method - Google Patents
A kind of municipal sludge compositing system and method Download PDFInfo
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- CN108059497A CN108059497A CN201711206164.XA CN201711206164A CN108059497A CN 108059497 A CN108059497 A CN 108059497A CN 201711206164 A CN201711206164 A CN 201711206164A CN 108059497 A CN108059497 A CN 108059497A
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
- C05F17/989—Flow sheets for biological or biochemical treatment
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F7/00—Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
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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 present invention discloses a kind of municipal sludge compositing system and method, including：Wet mud storage device, mixing device, fermentation subsystem, screening plant, wet mud is sent from wet mud storage device to mixing device through sludge transporting pipeline, and carry out mixing treatment with stalk and clinker, mixed material is transmitted to fermentation subsystem through belt feeder, earlier fermentation by using scattered supply aerator forced ventilation, the fermentation later stage is added using forced ventilation turns over throwing oxygen supply, it is transported after fermentation to screening plant, oversize after screening is re-fed into mixing device as clinker by belt feeder, screenings discharge carries out subsequent processing, further, further include deodorization subsystem.By the system and method, the oxygen demand and water content of heap body can be controlled well, the moisture content of sludge is made to be down to less than 30% by 80%, and the tail gas of generation can be collected and be reprocessed, qualified discharge after processing does not influence ambient enviroment.
Description
Technical field
The invention belongs to technical field of sludge treatment, and in particular to a kind of new sludge composting system and method.
Background technology
With the development of the city, the status of environmental protection also will be increasingly important.And with treatment rate of domestic sewage improve and
Caused sludge yield increases substantially, but also the process problem of sludge is more prominent.
Inorganic, organic pollution of the sludge due to containing concentration, also containing substantial amounts of pathogen and detection device for multi metallic elements,
Therefore, it is necessary to sludge is dealt carefully with.Treatment of Sludge seeks to carry out sludge depth harmless treatment, thoroughly solves dirty
Pollution of the mud to environment and the harm to the mankind.By specific resistance to filtration method sewage sludge can be made to reach minimizing, nothing
Evilization, the purpose of recycling.
The municipal sludge progress advanced treating arranged outside city is developed as the second energy resource just seems outstanding
To be important, the specific resistance to filtration scheme of effective, reasonable low consumption especially how is taken in force, will necessarily be brought out
The benefits such as source, throttling, environmental protection, economy and society.Municipal sludge is made to obtain effectively processing and the utilization of recycling, sludge
Fertile link is inevitable and the important step of specific resistance to filtration.
Existing sludge composting method is static compost, and traditional composting mode can generate foul smell, environment is caused secondary
Pollution, high risks are caused to the health of surrounding resident；Sludge disintegration is incomplete, and quality of compost products is low, recycling profit
It is low with rate；Automatization level is relatively low, and occurrence probability of safety accidents is higher.
The content of the invention
To solve the problems, such as specific resistance to filtration, the present invention provides a kind of new sludge composting system and method, suitable for city
The processing disposal of political affairs sludge, especially suitable for the place for the municipal sewage plant's municipal administration dewatered sludge being used in combination with landscape bureau of city
Reason disposal.
The present invention discloses a kind of municipal sludge compositing system, including：Wet mud storage device, mixing device, fermentation subsystem
System, screening plant,
Wet mud storage device：Including wet mud storage device body, screw pump and flow control valve, wet mud storage dress
Body is put with the first sludge inlet, sludge discharge hole, flow control valve and screw pump are arranged at sludge discharge hole, dirty
Mud discharge port connects mixing device by sludge transporting pipeline；
Mixing device：Including mixing device body and batch mixing rabbling mechanism, mixing device body has the second sewage sludge feed
Mouth, stalk feed inlet, clinker reflux inlet and batch mixing discharge port, the second sludge inlet are gone out by sludge transporting pipeline and sludge
Material mouth connects, and batch mixing discharge port connects fermentation subsystem by belt feeder；
Fermentation subsystem：Including installation for fermenting, for the compost in installation for fermenting turn over throw oxygen supply turn over polishing apparatus,
And the aerator of oxygen needed for fermentation is provided for the compost in installation for fermenting；
Screening plant：Including screening plant body, oversize discharge port, screenings discharge port, sieve from fermentation subsystem
Transport come it is fermented after mixed material.
As a preferred embodiment, the first sludge inlet is arranged on the top of wet mud storage device, sludge discharge hole
The bottom of wet mud storage device is arranged on, the bottom of wet mud storage device is in cone structure, is matched somebody with somebody at the first sludge inlet
It is equipped with hermatic door；It is also configured with preventing the sieve plate that bulk foreign matter enters at first sludge inlet.
As a preferred embodiment, mixing device body also has clinker reflux inlet；Screening plant will by belt feeder
Oversize after screening is re-fed into the clinker reflux inlet of mixing device, screenings discharge as clinker by belt feeder
Carry out subsequent processing.
As a preferred embodiment, the stalk feed inlet on mixing device and clinker reflux inlet are set to same and are mixed into
Mouthful.
As a preferred embodiment, installation for fermenting has multiple mutually independent fermentation units, and aerator has multiple
Mutually independent aeration unit, aeration unit are corresponded with fermentation unit, and the oxygen needed for fermentation is provided for each fermentation unit.
As a preferred embodiment, aeration unit includes centrifugal blower and the ventilation blower for being arranged in fermentation unit bottom
Structure；Centrifugal blower provides oxygen needed for fermentation by ventilating mechanisms for fermentation unit；Centrifugal blower is connected with to control it logical
The temperature of air quantity-oxygen intelligence control system, to ensure that fermentation is at one's best always.
As a preferred embodiment, installation for fermenting is also configured with distributing device, and the mixed material that belt feeder is sent is equal
Even point is put into each fermentation unit.
As a preferred embodiment, the inner wall of each fermentation unit is equipped with monitoring device placing groove, for placing temperature/oxygen
Gas monitoring device.
As a preferred embodiment, deodorization subsystem is further included, is configured with deodorization air hose, deodorization wind turbine, biofilter
With multiple air draught components, the tail gas of each device generation is adsorbed by air draught component, and passes through deodorization air hose and the collection of deodorization wind turbine
Tail gas, and tail gas is passed through biofilter and is filtered taste removal processing.
Invention additionally discloses a kind of municipal sludge compost methods, use the municipal sludge compost with above-mentioned technical characteristic
System includes the following steps：
Wet mud is transported to storing at wet mud storage device；
Screw pump output of the wet mud through wet mud storage device bottom, conveys through flow control valve and sludge transporting pipeline
To mixing device；In mixing device, stalk and clinker are automatically fed into mixing device by belt feeder and are carried out together with wet mud
Mixing treatment, the mixed material after mixing treatment are transmitted to fermentation subsystem automatically by belt feeder；
In fermentation treatments, earlier fermentation is each fermentation by using the aerator forced ventilation of scattered supply
Device provides the oxygen needed for fermentation；Fermenting, the later stage, also by turning over, polishing apparatus is periodical to fill fermentation on the basis of forced ventilation
Material in putting carries out turning over throwing, is turned over contact of the throwing process with air using material and realizes abundant aeration；Centrifugal blower passes through
Temperature-oxygen intelligence control system controls its ventilation quantity, to ensure that fermentation is at one's best always；
After fermentation, material is sent to screening plant by transporter and carries out screening process, on sieve after screening
Object is re-fed into mixing device as clinker by belt feeder, and screenings discharge carries out subsequent processing.
The invention has the advantages that：
(1) moisture percentage in sewage sludge and fermentation period, oxygen supply ventilation, compost temperature scope it is relatively corresponding, fermentation subsystem is adopted
It is fermentation oxygen supply with the mode for throwing oxygen supply and forced ventilation combination is turned over, using aerobic microbiological, and passes through temperature-oxygen and intelligently control
The ventilation quantity of centrifugal blower controls the oxygen demand and water content of heap body in system control aerator processed, makes containing for sludge
Water rate is down to less than 30% by 80%.
(2) sludge inlet of mixing device is that the circular port being adapted with sludge transporting pipeline size designs, and sludge leads to
The sludge transporting pipeline for crossing closing is directly entered mixing device and is mixed with stalk and clinker, and reduction foul smell leaks；Clinker passes back into
Mouth and stalk feed inlet are designed to same entrance, reduce mixing device opening, the foul smell generated in disposal process is through closed receipts
Collection reduces foul smell discharge capacity；And the tail gas of generation is collected and reprocessed further combined with biological deodorizing subsystem, it handles
Qualified discharge afterwards does not influence ambient enviroment.
(3) total system forms automatic transmission system by belt feeder, and high degree of automation saves manpower and reduces safety
Accident odds.
(4) the semi-oriented sludge product less than 30% moisture content after compost can make packed organic fertilizer by retrofit
Product directly does afforestation, Nutrition Soil use, realizes recycling sludge and innoxious purpose.
Description of the drawings
Fig. 1 is the municipal sludge compositing system composition schematic diagram disclosed in embodiment；
Fig. 2 is the structure diagram of the batch mixer disclosed in embodiment；
Fig. 3 is the structure diagram of the fermentation tank disclosed in embodiment；
Fig. 4 is the technical process schematic diagram of the municipal sludge compost method disclosed in embodiment；
Attached drawing marks：
Store workshop 1, material mixing workshop 2, fermentation plant 3, screen house 4；
Electric cabin door 11, wet hopper dredger 12, feed inlet 121, hermatic door 122, sieve plate 123, discharge port 124, sludge carrier pipe
Road 13, flow control valve 14, screw pump 15；
Batch mixer 21, sludge inlet 211, clinker reflux inlet/stalk feed inlet 212, discharge port 213, belt feeder 22,
Belt feeder 23；
Fermentation tank 31, turner 32, inclination angle belt conveyor 33, horizontal belt machine 34, ventilation duct 35, centrifugal blower 36, temperature
Degree/oxygen monitoring device 37, loading machine 38；
Screening machine 41, belt feeder 42；
Suspended hood 51, ventilation shaft 52, deodorization wind turbine 53, biofilter 54.
Specific embodiment
The present invention will be further described with reference to the accompanying drawings and examples.
With reference to shown in Fig. 1 to Fig. 3, the municipal sludge compositing system disclosed in embodiment mainly includes wet mud storage dress
It puts, mixing device, fermentation subsystem, screening plant and deodorization subsystem.
In storage workshop 1, mainly include electric cabin door 11, wet hopper dredger 12,13 flow control valve 14 of sludge transporting pipeline
With screw pump 15.
Wet hopper dredger 12 is arranged in below earth's surface, and sludge transport vehicle is facilitated directly to be poured onto wet mud in wet hopper dredger 12.It is wet
The feed inlet 121 at 12 top of hopper dredger is equipped with a hermatic door 122, which can be used pneumostop door or hydrodynamic seal
Door, for preventing peculiar smell from escaping；Sieve plate 123 is also set up at feed inlet 121, for bulk foreign matter to be prevented to be directly entered wet hopper dredger
12；The bottom of wet hopper dredger 12 is pyramidal structure, and flow control valve 14 and two screw rods are provided at the discharge port 124 of conical lower portion
Pump 15, by the collective effect of flow control valve 14 and two screw pumps 15, the wet mud of output can continuous, average rate, volume perseverance
Surely 13 automatic transport of sludge transporting pipeline to material mixing workshop 2 is passed through.
In material mixing workshop 2, mainly include batch mixer 21, belt feeder 22 and belt feeder 23.
Batch mixer 21 has sludge inlet 211, clinker reflux inlet/stalk feed inlet 212 and discharge port 213, clinker
Two belt feeders, i.e. belt feeder 22 and belt feeder 23 are disposed at reflux inlet/stalk feed inlet 212, as external conveying
Clinker and stalk (for example, the agricultural crop straws such as wheat, rice, corn) are introduced batch mixing by equipment respectively by two belt feeders
Machine 21.What deserves to be explained is in embodiment, clinker reflux inlet and batch mixer stalk feed inlet are designed to same entrance,
Its advantage is to reduce batch mixer opening, reduces foul smell amount, in specific application, can also set respectively as needed two it is different
Entrance is connected respectively with two belt feeders.Wet mud is through sludge transporting pipeline 13 automatically into the sludge inlet of batch mixer 21
211；Stalk is sent by belt feeder 22 to clinker reflux inlet/stalk feed inlet 212 after crusher in crushing；Sludge composting product by
After the sieve material of screening machine 41 of screen house 4, clinker reflux inlet/stalk that oversize is sent into batch mixer 21 through belt feeder 23 is fed
Mouth 212；Wet mud, stalk and oversize carry out mixing treatment in batch mixer 21；Mixed material is defeated from batch mixer discharge port 213
After going out, successively fermentation plant 3 is delivered to through high angle belt conveyer 33 and the biography of horizontal belt 34.
In fermentation plant 3, mainly include fermentation tank 31, turner 32, aeration unit 35, centrifugal blower 36, temperature/oxygen
Gas monitoring device 37 and loading machine 38.
With reference to shown in Fig. 3, fermentation tank 31 includes multiple independent fermentation units, and fermentation tank 31 is designed to groove width 4.5m, slot
High 2.5m, groove body length can be set according to mud handling capacity.Slot bottom arranges three ventilation ducts 35, and ventilation duct 35 is uniformly distributed,
Every 1.5m, ventilation duct 35 has multiple equally distributed ventilation holes, ensures uniformly to supply oxygen for heap body each several part, heap body is made fully to send out
Ferment.Centrifugal blower 36 is corresponded with fermentation tank 31, i.e., separate unit centrifugal blower 36 supplies single fermentation tank 31, with decentralised control
Composting fermentation process in each fermentation tank 31.The cell wall of fermentation tank 31 is provided with monitoring device placing groove, is inside disposed with temperature spy
Survey/oxygen monitoring device 37 for the on-line monitoring of material oxygen content and temperature, controls aeration quantity, and effective guarantee ferments always
At one's best, monitoring device placing groove can be evenly arranged according to the length of fermentation tank 31.Now in the art, usually by temperature
Detection/oxygen monitoring device 37 is directly inserted in fermentation tank 31 (i.e. in sludge), in practical application, turning over throwing every time will pull out
Out, as a preferred embodiment, the monitoring device for outputing suitable dimension size in embodiment at the cell wall of fermentation tank 31 is placed
Slot, and temperature sensing/oxygen monitoring device 37 is arranged in monitoring device mounting groove, sludge and temp probe contact/gas
By oxygen sensor, the digital signal that electric signal generates temperature/oxygen concentration through transmitter is generated, passes through conveying circuit in real time
It is stored by computer acquisition to capture card, and is shown simultaneously in display.32 preferred BACKHUS turners of turner, BACKHUS
Turner can make full use of oneself body advantage, clean out Crane Rail by track cleaning device, roller is variable speed, also may be used
It reverses, ground will not be encountered during turning.Using BACKHUS control systems, i.e. excess load track drive control system
System, can also automatically adjust operation intensity under event of overload.It, can be in unevenness with track cleaning device and mating flusher
, travelled on soft ground.ZL50 forklifts can be selected in loading machine 38, pass through diesel driven.
In screen house 4, mainly include screening machine 41, belt feeder 42.Compost passes through loading after fermented workshop 3 is handled
Machine 38 is transported to screen house 4.
Above each workshop is by functional regional division, and to prevent the tail gas in workshop excessive, which is also provided with deodorization
System mainly includes suspended hood 51, ventilation shaft 52, deodorization wind turbine 53 and biofilter 54.Suspended hood 51 is arranged in storage vehicle
Between 1, material mixing workshop 2, the top of fermentation plant 3, each suspended hood 51 is connected to the ventilation shaft 52 at top, then by deodorization wind turbine 53
It send to biofilter 54.Pass through the deodorization subsystem, material basic free from extraneous odour after everfermentation.
With reference to shown in Fig. 4, the specific workflow of wet mud compost is as follows：
Wet mud is poured onto the wet hopper dredger 12 being arranged in below earth's surface by sludge transport vehicle, and wet 12 top of hopper dredger is semi-closure
Half opening device, electric cabin door 11 is automatically closed after dumping, and is equipped with gas detecting instrument, for example, combustible gas alarming instrument.It is wet
Sludge enters wet hopper dredger 12 by the sieve plate 123 that wet 12 top of hopper dredger is set.It after storing, can be by being set at discharge port 124
14 conditioning of mud of flow control valve load, and pass through two screw pumps 15 and export wet mud, the wet mud of output is again
It is continuous, average rate, constant volume into the progress mixing treatment of material mixing workshop 2 by sludge transporting pipeline 13.
Wet mud enters batch mixer 21 through sludge inlet 211, and stalk is sent by belt feeder 22 to batch mixing after crusher in crushing
Machine stalk feed inlet 212, after the screened sieve of machine 41 of sludge composting product is expected, oversize is sent into the ripe of batch mixer 21 through belt feeder 23
Expect that reflux inlet 212 carries out mixing treatment, the mixed material after mixing treatment is exported by the discharge port 213 of batch mixer 21, gone out
High angle belt conveyer 33 is connect under material mouth 213,33 lower accepting water flat belt 34 of high angle belt conveyer, mixed material is by high angle belt conveyer 33 and water
Flat belt 34 is transmitted to fermentation plant 3 and ferments.
Fermentation plant turns over throwing mode using trough composting, using whole input and output material technique.Mixed material through belt feeder send to
The fermentation tank 31 of fermentation plant 3, through distributing device uniform distribution until groove body piles with.Using turning over, throwing supplies oxygen and pressure is logical during fermentation
The mode that wind combines supplies oxygen for fermentation, and forced ventilation, turner are realized by using the aerator of scattered supply in the fermentation phase
32 periodically carry out heap body to turn over throwing, ensure one day turning ability at least once.Specifically, daily charging is disposably placed in
One or more of one fermentation tank 31 fermentation unit, entire slot is not by the way of carrying out returning and throwing, in entire fermentation period
Into new material, wait once to discharge after the completion of fermenting.Turner 32 uses diesel oil as fuel, walks in the cell wall of fermentation tank 31
On, forward and reverse walking while, carries out turning over throwing, and throwing is turned over so as to fulfill shuttle.Turner 32 can set daily turning and throwing once,
The contact with air in a flash of throwing is turned over using material and realizes oxygenation, ensures to be turned over the uniform and abundant aeration of cast material,
The dead angle of sweathouse is avoided, improves the stability of compost.It is only oxygenated, is then inevitably led by turning over throwing in fermentation process
The most of the time is caused to there are problems that anaerobism, so as to cause stench and the environmental sanitation problem of mosquitos and flies, for oxygen is overcome to supply hypoxgia
The shortcomings that, in above process, referred to using forced ventilation in fermentation plant 3 by being supplied in fermentation plant 3 using scattered
Aerator come the shortcomings that further overcoming fermentation subsystem oxygen oxygen supply deficiency, by 31 bottom of fermentation tank along length side
To the ventilation duct 35 (can also be ventilation slot) of setting, supplied by centrifugal blower 36.Aerator uses temperature-oxygen
Intelligence control system controlled, the blow rate required of combining with fermentation time control centrifugal blower 36 and contains oxygen demand to heap body
Water carries out a degree of control, and it is at one's best always that fermentation is effectively ensured.
After fermentation, material is sent to screen house 4, screened machine by loading machine 38 less than 30% moisture content compost
Oversize after 41 screenings send to the clinker reflux inlet of batch mixer 21/stalk feed inlet 212 through belt feeder 23 and carries out back-mixing, sieve
Lower object makes packed organic fertilizer product by retrofit or directly does afforestation, Nutrition Soil use, realizes recycling sludge
With innoxious purpose.
In above process, the tail gas that each workshop generates in composting process is removed by deodorization subsystem, in storage workshop
1st, material mixing workshop 2, in fermentation plant 3, storage workshop 1, material mixing workshop 2, the deodorization air hose of fermentation plant 3 and removing for compost workshop
Smelly air hose is connected.The foul smell that compost generates is sent by deodorization wind turbine 53 to biology again after being adsorbed by suspended hood 51 through deodorization air hose 52
Filter tank 54 is filtered taste removal, with rear discharge up to standard.
The foregoing is only a preferred embodiment of the present invention, is not intended to limit the invention, for the skill of this field
For art personnel, the invention may be variously modified and varied.Within the spirit and principles of the invention, that is made any repaiies
Change, equivalent substitution, improvement etc., should all be included in the protection scope of the present invention.
Claims (10)
1. a kind of municipal sludge compositing system, which is characterized in that including：Wet mud storage device, mixing device, fermentation subsystem
System, screening plant,
The wet mud storage device includes wet mud storage device body, screw pump and flow control valve, wet mud storage dress
Body is put with the first sludge inlet, sludge discharge hole, flow control valve and screw pump are arranged at sludge discharge hole, dirty
Mud discharge port connects mixing device by sludge transporting pipeline；
The mixing device includes mixing device body and batch mixing rabbling mechanism, and mixing device body has the second sewage sludge feed
Mouth, stalk feed inlet, clinker reflux inlet and batch mixing discharge port, the second sludge inlet are gone out by sludge transporting pipeline and sludge
Material mouth connects, and batch mixing discharge port connects fermentation subsystem by belt feeder；
The fermentation subsystem includes installation for fermenting, for the compost in installation for fermenting turn over throw oxygen supply turn over polishing apparatus,
And the aerator of oxygen needed for fermentation is provided for the compost in installation for fermenting；
The screening plant includes screening plant body, oversize discharge port, screenings discharge port, sieves and is transported from fermentation subsystem
It is defeated come it is fermented after mixed material.
2. municipal sludge compositing system as described in claim 1, which is characterized in that first sludge inlet is arranged on wet
The top of sludge storage device, the sludge discharge hole are arranged on the bottom of wet mud storage device, the wet mud storage dress
The bottom put is in cone structure, and hermatic door is configured at the first sludge inlet；It is also configured at first sludge inlet
For preventing the sieve plate of bulk foreign matter entrance.
3. municipal sludge compositing system as described in claim 1, which is characterized in that the mixing device body also has clinker
Reflux inlet；The screening plant is regard oversize after screening as clinker by belt feeder and is re-fed by belt feeder
The clinker reflux inlet of mixing device, screenings discharge carry out subsequent processing.
4. municipal sludge compositing system as claimed in claim 3, which is characterized in that the stalk feed inlet on the mixing device
Same mixing entrance is set to clinker reflux inlet.
5. municipal sludge compositing system as described in claim 1, which is characterized in that the installation for fermenting has multiple mutually only
Vertical fermentation unit, the aerator have multiple mutually independent aeration units, and aeration unit is a pair of with fermentation unit one
Should, provide the oxygen needed for fermentation for each fermentation unit.
6. municipal sludge compositing system as claimed in claim 5, which is characterized in that the aeration unit include centrifugal blower with
And it is arranged in the ventilating mechanisms of fermentation unit bottom；Centrifugal blower provides fermentation requisite oxygen by ventilating mechanisms for fermentation unit
Gas；Centrifugal blower is connected with to control temperature-oxygen intelligence control system of its ventilation quantity, to ensure that fermentation is in most always
Good state.
7. municipal sludge compositing system as claimed in claim 5, which is characterized in that the installation for fermenting is also configured with cloth
Device, the mixed material that belt feeder is sent, which uniformly divides, is put into each fermentation unit.
8. municipal sludge compositing system as claimed in claim 5, which is characterized in that the inner wall of the fermentation unit is equipped with prison
Device placing groove is surveyed, for placing temperature/oxygen monitoring device.
9. municipal sludge compositing system as described in claim 1, which is characterized in that further include deodorization subsystem, be configured with
Deodorization air hose, deodorization wind turbine, biofilter and multiple air draught components adsorb the tail gas of each device generation by air draught component, and
Tail gas is collected by deodorization air hose and deodorization wind turbine, and tail gas is passed through biofilter and is filtered taste removal processing.
10. a kind of municipal sludge compost method, which is characterized in that dirty using the municipal administration as described in claim 1 to 9 any one
Mud compositing system, includes the following steps：
Wet mud is transported to storing at wet mud storage device；
Screw pump output of the wet mud through wet mud storage device bottom, is delivered to mixed through flow control valve and sludge transporting pipeline
Expect device；In mixing device, stalk and clinker are automatically fed into mixing device by belt feeder and carry out batch mixing together with wet mud
It handles, the mixed material after mixing treatment is transmitted to fermentation subsystem automatically by belt feeder；
In fermentation treatments, earlier fermentation is each installation for fermenting by using the aerator forced ventilation of scattered supply
Oxygen needed for fermentation is provided；The fermentation later stage is on the basis of forced ventilation also by turning over polishing apparatus periodically in installation for fermenting
Material carry out turning over throwing, turned over contact of the throwing process with air using material and realize abundant aeration；Centrifugal blower by temperature-
Oxygen intelligence control system controls its ventilation quantity, to ensure that fermentation is at one's best always；After fermentation, filled by transporting
It puts to send material to screening plant and carries out screening process, oversize after screening is re-fed into as clinker by belt feeder
Mixing device, screenings discharge carry out subsequent processing.
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Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108997037A (en) * | 2018-08-10 | 2018-12-14 | 江苏思威博生物科技有限公司 | A kind of municipal sludge compositing system |
| CN109776237A (en) * | 2019-01-25 | 2019-05-21 | 北京海斯顿水处理设备有限公司 | A kind of charcoal base manure fermentation system and fermentation process |
| CN110467486A (en) * | 2019-09-02 | 2019-11-19 | 河北工程大学 | A kind of automation integrated composting device |
| CN112830834A (en) * | 2021-03-09 | 2021-05-25 | 湖南屎壳郎环境科技有限公司 | Aerobic fermentation treatment system |
| CN112845543A (en) * | 2021-03-09 | 2021-05-28 | 湖南屎壳郎环境科技有限公司 | Horizontal high-temperature aerobic fermentation reaction system |
| CN113185333A (en) * | 2021-05-20 | 2021-07-30 | 江西中江环保集团股份有限公司 | Municipal sludge composting method |
| CN113337441A (en) * | 2021-06-24 | 2021-09-03 | 哈尔滨工业大学 | High-temperature-resistant sulfur oxidizing strain LYH-2 and application thereof |
| CN113354456A (en) * | 2021-06-19 | 2021-09-07 | 宁夏大学 | Method for preparing sludge organic fertilizer and seedling culture substrate formula |
| CN115028485A (en) * | 2022-06-07 | 2022-09-09 | 河海大学 | Sludge composting recycling device |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102557368A (en) * | 2010-12-20 | 2012-07-11 | 机科发展科技股份有限公司 | High-temperature aerobic composting treatment process for municipal sludge |
| CN103044105A (en) * | 2013-01-05 | 2013-04-17 | 北京中持绿色能源环境技术有限公司 | Treatment system and treatment method for continuous dynamic aerobic fermentation of organic waste |
| CN202988933U (en) * | 2012-12-14 | 2013-06-12 | 首大能源环保集团有限公司 | Sludge treatment land resource utilization system |
| CN104478511A (en) * | 2014-12-25 | 2015-04-01 | 南京道科环境科技有限公司 | Efficient device and treatment method for compostingurbandomestic sludge |
| CN106431553A (en) * | 2016-11-22 | 2017-02-22 | 新疆天物生态科技股份有限公司 | High-temperature aerobic fermentation sludge compost treatment and disposal system |
| CN106431547A (en) * | 2016-11-02 | 2017-02-22 | 北京合清环保技术有限公司 | Aerobic fermentation device adopting aeration trolleys for transferring materials |
| CN206396069U (en) * | 2017-01-09 | 2017-08-11 | 中城环境技术（天津）有限公司 | Sludge dynamically accelerates aerobic high-heat fermented manure equipment |
-
2017
- 2017-11-27 CN CN201711206164.XA patent/CN108059497A/en active Pending
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102557368A (en) * | 2010-12-20 | 2012-07-11 | 机科发展科技股份有限公司 | High-temperature aerobic composting treatment process for municipal sludge |
| CN202988933U (en) * | 2012-12-14 | 2013-06-12 | 首大能源环保集团有限公司 | Sludge treatment land resource utilization system |
| CN103044105A (en) * | 2013-01-05 | 2013-04-17 | 北京中持绿色能源环境技术有限公司 | Treatment system and treatment method for continuous dynamic aerobic fermentation of organic waste |
| CN104478511A (en) * | 2014-12-25 | 2015-04-01 | 南京道科环境科技有限公司 | Efficient device and treatment method for compostingurbandomestic sludge |
| CN106431547A (en) * | 2016-11-02 | 2017-02-22 | 北京合清环保技术有限公司 | Aerobic fermentation device adopting aeration trolleys for transferring materials |
| CN106431553A (en) * | 2016-11-22 | 2017-02-22 | 新疆天物生态科技股份有限公司 | High-temperature aerobic fermentation sludge compost treatment and disposal system |
| CN206396069U (en) * | 2017-01-09 | 2017-08-11 | 中城环境技术（天津）有限公司 | Sludge dynamically accelerates aerobic high-heat fermented manure equipment |
Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108997037A (en) * | 2018-08-10 | 2018-12-14 | 江苏思威博生物科技有限公司 | A kind of municipal sludge compositing system |
| CN109776237A (en) * | 2019-01-25 | 2019-05-21 | 北京海斯顿水处理设备有限公司 | A kind of charcoal base manure fermentation system and fermentation process |
| CN110467486A (en) * | 2019-09-02 | 2019-11-19 | 河北工程大学 | A kind of automation integrated composting device |
| CN110467486B (en) * | 2019-09-02 | 2022-04-08 | 河北工程大学 | Automatic change integrative compost device |
| CN112830834A (en) * | 2021-03-09 | 2021-05-25 | 湖南屎壳郎环境科技有限公司 | Aerobic fermentation treatment system |
| CN112845543A (en) * | 2021-03-09 | 2021-05-28 | 湖南屎壳郎环境科技有限公司 | Horizontal high-temperature aerobic fermentation reaction system |
| CN112845543B (en) * | 2021-03-09 | 2024-01-23 | 湖南屎壳郎环境科技有限公司 | Horizontal high-temperature aerobic fermentation reaction system |
| CN113185333A (en) * | 2021-05-20 | 2021-07-30 | 江西中江环保集团股份有限公司 | Municipal sludge composting method |
| CN113354456A (en) * | 2021-06-19 | 2021-09-07 | 宁夏大学 | Method for preparing sludge organic fertilizer and seedling culture substrate formula |
| CN113337441A (en) * | 2021-06-24 | 2021-09-03 | 哈尔滨工业大学 | High-temperature-resistant sulfur oxidizing strain LYH-2 and application thereof |
| CN113337441B (en) * | 2021-06-24 | 2022-08-09 | 哈尔滨工业大学 | High-temperature-resistant sulfur oxidizing strain LYH-2 and application thereof |
| CN115028485A (en) * | 2022-06-07 | 2022-09-09 | 河海大学 | Sludge composting recycling device |
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