CN206337182U - Sludge high temperature aerobic fermented manure handles disposal system - Google Patents
Sludge high temperature aerobic fermented manure handles disposal system Download PDFInfo
- Publication number
- CN206337182U CN206337182U CN201621258450.1U CN201621258450U CN206337182U CN 206337182 U CN206337182 U CN 206337182U CN 201621258450 U CN201621258450 U CN 201621258450U CN 206337182 U CN206337182 U CN 206337182U
- Authority
- CN
- China
- Prior art keywords
- sludge
- temperature aerobic
- high temperature
- fermentation
- aerobic fermentation
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
Classifications
-
- 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
Landscapes
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Abstract
The utility model belongs to harmless treatment and the application technology as the second resource field of organic solid waste resource, specifically related to a kind of sludge high temperature aerobic fermented manure processing disposal system, including sludge preprocessing system and sludge composting fermenting process control system, the sludge preprocessing system is used to conveying sludge, batch mixing and high-temperature aerobic fermentation, the sludge composting fermenting process control system is used for online acquisition sludge high temperature aerobic Fermentation Process of Parameter, and high-temperature aerobic fermentation sludge is carried out according to the procedure parameter to turn over throwing and ventilation treatment, to control fermentation process.The utility model is by controlling the process of Sewage Sludge in Composting, adjust the optimal yeastiness of material, play and organic matter and given off energy in profitable strain action breaks sludge, reach the effect for killing harmful pathogen, final product active constituent content and microbiological indicator meet agricultural standards, finally realize the minimizing of sludge, innoxious, recycling.
Description
Technical field
The utility model belongs to harmless treatment and the application technology as the second resource field of organic solid waste resource, and in particular to one
Plant sludge high temperature aerobic fermented manure processing disposal system.
Background technology
A large amount of undressed sludge are arbitrarily stacked and discharged, and can not only waste the useful nutrient in sludge, can also be to ring
Cause new pollution in border.Therefore, how by yield is big, complicated component sludge by scientific disposal make its minimizing, it is innoxious,
Recycling and stabilisation, it has also become one of problem that China or even whole world environment circle are paid close attention to jointly.Agricultural sludge small investment, energy
The low, operating cost of consumption is low, and some of which part can be converted into the composition of soil conditioner, therefore agricultural sludge is considered as very
There are a kind of disposal options of development potentiality.But, sludge components are extremely complex, not only containing abundant organic matter and many plants
The nutritional ingredient such as trace element necessary to growth, also containing a large amount of pathogens, parasite (ovum), the huge sum of money such as copper, zinc, chromium, mercury
Category, the venomous injurant of the difficult degradation such as salt and Polychlorinated biphenyls, bioxin, radionuclide directly carries out agricultural have very
Big risk, it is necessary to which being carried out to sludge can be agricultural after thoroughly harmless treatment disposal, therefore, needs a kind of new science badly
Sludge aerobic compost handles disposal system, to be regional sludge rationally and effectively using technology mode is provided, set up and be adapted to city
City's sludge treatment and the effective way utilized.
Utility model content
The purpose of this utility model is to provide a kind of sludge high temperature aerobic fermented manure processing disposal system, with solution
State problem.
Embodiment of the present utility model provides a kind of sludge high temperature aerobic fermented manure and handles disposal system, including sludge
Preprocessing system and sludge composting fermenting process control system, sludge preprocessing system be used for sludge is conveyed, batch mixing and
High-temperature aerobic fermentation, sludge composting fermenting process control system is used for online acquisition sludge high temperature aerobic Fermentation Process of Parameter, and
High-temperature aerobic fermentation sludge is carried out according to procedure parameter to turn over throwing and ventilation treatment, to control fermentation process；Wherein, sludge high temperature
Aerobic fermentation procedure parameter includes pH value, temperature, humidity, oxygen content, ammonia level, hydrogen sulfide content.
Further, the system also includes recycling reprocessing system, and recycling reprocessing system is used for the dirt to fermenting
Mud material is sieved, after dewater treatment, prepares organic fertilizer.
Further, sludge preprocessing system includes conveying device and mixing arrangement；Conveying device is used in sludge bin
Pending mud is delivered to mixing arrangement and carries out batch mixing, and the sludge after batch mixing is delivered into fermentation tank progress high-temperature aerobic hair
Ferment.
Further, sludge composting fermenting process control system includes data acquisition conveying device, middle control platform, gas distribution dress
Put, turn over polishing apparatus, on-line monitoring device；Data acquisition conveying device is used to gather sludge high temperature aerobic Fermentation Process of Parameter, and
Middle control platform is transported to, middle control platform is used to start distribution device according to sludge high temperature aerobic Fermentation Process of Parameter and turns over throwing
Device carries out gas distribution and turns over throwing processing, and on-line monitoring device is used to carry out sludge high temperature aerobic fermentation process in online prison in real time
Control.
Further, the system also includes odor removal, and odor removal is used for the ammonia in high-temperature aerobic fermentation sludge
Content and hydrogen sulfide content, by it is middle control platform courses aspirated, deodorizing process.
Further, the system also includes batch mixing control device, and batch mixing control device is controlled for batch mixing, including is come to conveying
Sludge and auxiliary material mixed, conditioning of mud, auxiliary material moisture, carbon-nitrogen ratio physicochemical property reach aerobic fermentation condition, and add
Decomposing microbial inoculum.
Further, recycling reprocessing system includes screening plant, and screening plant is used to enter the sludge material fermented
Row screening process, screenings is dehydrated to less than 30%, and for preparing organic fertilizer, oversize is expected as fermentation backfill, conveyed,
Batch mixing and high-temperature aerobic fermentation.
The beneficial effects of the utility model are compared with prior art：By controlling the process of Sewage Sludge in Composting,
The optimal yeastiness of material is adjusted, plays and organic matter and is given off energy in profitable strain action breaks sludge, reach that killing has
Evil bacterium and the effect of virus, final product active constituent content and microbiological indicator meet agricultural standards, finally realize sludge
Minimizing, innoxious, recycling.
Brief description of the drawings
Fig. 1 is the process chart of the embodiment of the utility model one.
Embodiment
The utility model is described in detail shown each embodiment below in conjunction with the accompanying drawings, but it should explanation,
These embodiments are not limitation of the utility model, and those of ordinary skill in the art are according to these embodiment institute works
Energy, method or equivalent transformation or replacement in structure, are belonged within protection domain of the present utility model.
The sludge high temperature aerobic fermented manure processing disposal system that the present embodiment is provided, is broadly divided into eight big subsystems：It is defeated
Send system, mixing system, fermentation aerating system, turning system, central control system, Real-time and On-line, deodoration system and money
Source reprocessing system.The present embodiment utilizes induction system, metering device, by municipal sludge, special decomposing microbial inoculum, backfill
Auxiliary material is delivered to mixing system, after being sufficiently mixed to the material being delivered at batch mixer, then is transported to high temperature through induction system
High-temperature aerobic fermentation, thoroughly becoming thoroughly decomposed, harmless treatment are carried out in aerobic fermentation groove.Based on real time on-line monitoring system, pass through
Monitoring to fermentation parameters such as temperature, suitable humidity degree, dissolved oxygens, by central control system, real-time monitoring automatic aeration device and wireless controlled
Turning system processed, process control is carried out to fermented sludge.After the high-temperature aerobic fermentation of 15-18 days, carry out secondary 15-20 days
Digest process, thoroughly reaches the harmless treatment to municipal sludge afterwards.It is first that municipal sludge is generated after harmless treatment
Level Nutrition Soil, the carry out secondary operation of system is reprocessed by recycling, production gardens, woods fruit organic fertilizer are completed to city
The harmless treatment minimizing of domestic sludge and recycling.The system intelligent degree is high, reliable, processing cost
It is low.
Join shown in Fig. 1, Fig. 1 is the process chart of the embodiment of the utility model one, and the technological process shows the system
Pre-treatment, the technological process that utilizes of fermented manure Treatment and recovery.
1st, sludge pre-treatment, containing induction system (conveying device) and mixing system, mainly includes sludge bin 11, sludge defeated
Send the devices such as pump, auxiliary material conveyer belt, batch mixer and compound conveyer belt.
It is temporarily stored in entering factory's dewatered sludge (aqueous≤80%) in sludge bin 11, opens induction system, it is defeated by sludge
Pump is sent to export sludge from sludge bin 11, the communicated band conveying of auxiliary material, backfill material, by metering device, is delivered to mixing jointly
Area；Mixing system is opened, the material come by the conveying of 12 pairs of mixing arrangement is mixed, and conditioning of mud auxiliary material moisture, carbon-nitrogen ratio are managed
Change property, there is microbial inoculum meter to add special decomposing microbial inoculum during reaching aerobic fermentation condition, and mixing；
By batch mixing conveying device, mixed material, it is delivered in fermentation tank 13, carries out high-temperature aerobic fermentation.
2nd, sludge composting fermentation processes, containing Real-time and On-line, central control system, turning system, fermentation expose
Gas system, 5 subsystems of deodoration system, zymotechnique Based Intelligent Control can be carried out by above subsystem, and biofermentation is controlled, mixed
The Based Intelligent Controls such as material control, screening control and deodorization control.Specifically include, (online) data acquisition conveying device 21, middle control are flat
Platform 22, distribution device 23, turn over polishing apparatus 24, on-line monitoring device 26, deodorization device 25 and exhaust apparatus.
By batch mixing control, sludge, auxiliary material are carried out after the quenched end of mixing, as fermenting mixture material enters tankful, led to
Cross central control system regulation and control and turn over polishing apparatus 24 and fermentation materials are turned over throwings first, progress material is loose smooth, quick to provide microorganism
Growing environment；
Real-time and On-line (including data acquisition conveying device 21 and on-line monitoring device 26) is opened, by online
Data acquisition conveying device 21, carries out online acquisition transmission to pH, temperature, humidity, oxygen content, ammonia, hydrogen sulfide, passes through middle control
Platform 22 (zymotechnique intelligent control software) to data confluence analysis, open control fermentation aerating system (distribution device 23) and
Turning system (turning over polishing apparatus 24) carries out turning over throwing, ventilation treatment operation to sludge fermentation process, reaches and fermentation materials are put down
Whole, loose, ventilation, radiating, control material fermentation process adjust the optimal yeastiness of material；Deodoration system is opened, passes through ammonia
Gas, hydrogen sulfide foul smell detection conveyer, reach foul smell deodorization control system, start deodorization device 25, foul smell is carried out
Suction, deodorizing process.
In pretreatment stage, by mixing the bacteria agent and on-line plan of addition in mixing system, micro- life is utilized
Thing own metabolism heat production, the processing of (65-75 DEG C) of high temperature is carried out to sludge material, the wherein high-temperature process stage at 6-8 days, to sludge
In pathogen, roundworm egg thoroughly inactivated, and reaches to sludge material innoxious, minimizing purpose.
3rd, recycling process, system is reprocessed containing recycling.Induction system is opened, it is good to compost maturity in groove
Sludge material, communicated device is delivered to recycling scratchpad area (SPA), starts screening plant, to fermentations such as the sludge that fully becomes thoroughly decomposed
Material, screened device carries out screening process, and screenings is dehydrated to less than 30%, prepares organic fertilizer, carries out Land_use change, improvement
Soil.Oversize is as fermentation backfill material, and communicated device is delivered between batch mixing, into next fermentation process.
Below by concrete application example, the utility model is described in further detail.
The ton day specific resistance to filtration of Urumqi City east of a river sewage treatment plant 350.
Hedong Sewage Disposal Plant dispatches from the factory sludge, and aqueous 78%, there is sludge special transport vehicle to be transported to sludge treatment factory sludge storage bin,
Carry out interim storage；By induction system, batch mixing dress is delivered to sludge bin sludge and backfill material, the metering of stalk auxiliary material respectively
Put；Mixing system is opened, blending mix to uniformly to sludge, auxiliary material；Induction system is opened, uniform thing is mixed to ginseng
Material is delivered to fermentation tank and carries out fermented manure processing.Real-time and On-line is opened, passes through temperature, moisture, pH, oxygen, ammonia
Gas, hydrogen sulfide detector, in real time detection composting fermentation process parameter, data are sent to middle control platform, by central control system according to
Zymotechnique intelligent control software intellectual analysis, according to fermentation dynamic process, intelligent selection turning system, fermentation aerating system,
Deodoration system, which starts, turns over polishing apparatus, distribution device or odor removal, and fermentation process is regulated and controled, material During High-Temperature Composting shape is maintained
State.After compost fermentation in 16 days grooves, start conveyer through induction system and the good material of compost fermentation is stored to resource
Change utilizes area, through 20 days from then digest process, fermentation materials are carried out with screening process, screenings drying, garden is packaged into
Woods organic fertilizer, oversize is delivered to pretreatment process, mixed fermentation again as fermentation backfill material through conveying device backflow.
The a series of tool described in detail only for feasibility embodiment of the present utility model of those listed above
Body illustrates that they are simultaneously not used to limit protection domain of the present utility model, all to be made without departing from the utility model skill spirit
Equivalent implementations or change should be included within protection domain of the present utility model.
It is obvious to a person skilled in the art that the utility model is not limited to the details of above-mentioned one exemplary embodiment, and
And in the case of without departing substantially from spirit or essential attributes of the present utility model, can realize that this practicality is new in other specific forms
Type.Therefore, no matter from the point of view of which point, embodiment all should be regarded as exemplary, and is nonrestrictive, this practicality is new
The scope of type limits by appended claims rather than described above, it is intended that the equivalency fallen in claim is contained
All changes in justice and scope are included in the utility model.
Claims (7)
1. a kind of sludge high temperature aerobic fermented manure handles disposal system, it is characterised in that including sludge preprocessing system and dirt
Mud composting fermentation process control system, the sludge preprocessing system to sludge for being conveyed, batch mixing and high-temperature aerobic are sent out
Ferment, the sludge composting fermenting process control system is used for online acquisition sludge high temperature aerobic Fermentation Process of Parameter, and according to institute
State procedure parameter high-temperature aerobic fermentation sludge is carried out to turn over throwing and ventilation treatment, to control fermentation process；Wherein, the sludge is high
Warm aerobic fermentation procedure parameter includes pH value, temperature, humidity, oxygen content, ammonia level, hydrogen sulfide content.
2. sludge high temperature aerobic fermented manure according to claim 1 handles disposal system, it is characterised in that also including money
Source reprocessing system, recycling reprocessing system is used to sieving the sludge material fermented, after dewater treatment,
Prepare organic fertilizer.
3. sludge high temperature aerobic fermented manure according to claim 1 or 2 handles disposal system, it is characterised in that described
Sludge preprocessing system includes conveying device and mixing arrangement；The conveying device is used for the pending mud in sludge bin is defeated
Deliver to the mixing arrangement and carry out batch mixing, and the sludge after batch mixing is delivered to fermentation tank and carry out high-temperature aerobic fermentation.
4. sludge high temperature aerobic fermented manure according to claim 1 or 2 handles disposal system, it is characterised in that described
Sludge composting fermenting process control system include data acquisition conveying device, middle control platform, distribution device, turn over polishing apparatus, it is online
Supervising device；The data acquisition conveying device is used to gather the sludge high temperature aerobic Fermentation Process of Parameter, and is conveyed
To the middle control platform, the middle control platform is used to start the gas distribution dress according to the sludge high temperature aerobic Fermentation Process of Parameter
Put and turn over polishing apparatus to carry out gas distribution and turn over throwing processing, the on-line monitoring device is used to carry out sludge high temperature aerobic fermentation process
On line real-time monitoring.
5. sludge high temperature aerobic fermented manure according to claim 4 handles disposal system, it is characterised in that also including except
Smelly device, the odor removal is used for ammonia level and hydrogen sulfide content in high-temperature aerobic fermentation sludge, by described
Middle control platform courses are aspirated, deodorizing process.
6. sludge high temperature aerobic fermented manure according to claim 1 or 2 handles disposal system, it is characterised in that also wrap
Batch mixing control device is included, the batch mixing control device is controlled for batch mixing, including mixed to conveying the sludge come and auxiliary material,
Conditioning of mud, auxiliary material moisture, carbon-nitrogen ratio physicochemical property, reach aerobic fermentation condition, and add decomposing microbial inoculum.
7. sludge high temperature aerobic fermented manure according to claim 2 handles disposal system, it is characterised in that the resource
Changing reprocessing system includes screening plant, and the screening plant is used to carry out under screening process, sieve the sludge material fermented
Thing is dehydrated to less than 30%, for preparing organic fertilizer, and oversize is conveyed, batch mixing and high-temperature aerobic as fermentation backfill material
Fermentation.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201621258450.1U CN206337182U (en) | 2016-11-22 | 2016-11-22 | Sludge high temperature aerobic fermented manure handles disposal system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201621258450.1U CN206337182U (en) | 2016-11-22 | 2016-11-22 | Sludge high temperature aerobic fermented manure handles disposal system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN206337182U true CN206337182U (en) | 2017-07-18 |
Family
ID=59307869
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201621258450.1U Active CN206337182U (en) | 2016-11-22 | 2016-11-22 | Sludge high temperature aerobic fermented manure handles disposal system |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN206337182U (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108752067A (en) * | 2018-08-23 | 2018-11-06 | 新乡市逸凡蔚岚堆肥生物技术有限公司 | It is a kind of to slot type aerobic composting fermentation technology and its structure |
| CN110330201A (en) * | 2019-08-12 | 2019-10-15 | 泰安清源水务有限公司 | A kind of municipal sludge high temperature pure oxygen aeration fermentative production system and technique |
-
2016
- 2016-11-22 CN CN201621258450.1U patent/CN206337182U/en active Active
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108752067A (en) * | 2018-08-23 | 2018-11-06 | 新乡市逸凡蔚岚堆肥生物技术有限公司 | It is a kind of to slot type aerobic composting fermentation technology and its structure |
| CN110330201A (en) * | 2019-08-12 | 2019-10-15 | 泰安清源水务有限公司 | A kind of municipal sludge high temperature pure oxygen aeration fermentative production system and technique |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN106431553A (en) | High-temperature aerobic fermentation sludge compost treatment and disposal system | |
| CN102951939B (en) | Rapid harmless plant organic residue treatment and fertilizer utilization process and equipment thereof | |
| CN107117786A (en) | Plant's dejecta treatment method and system | |
| CN101665312B (en) | Livestock and poultry manure treating method | |
| CN101817702A (en) | Special bio-organic fertilizer for peaches and preparation method thereof | |
| CN106242669A (en) | A kind of biological organic fertilizer | |
| CN106278417A (en) | A kind of method utilizing municipal sludge to produce biological organic fertilizer | |
| CN107573111A (en) | A kind of method that organic domestic waste is handled using zymophyte aerobic compost | |
| CN105061004A (en) | Preparation method for biological organic fertilizer | |
| CN109020688A (en) | Anaerobism adds the method for aerobic fermentation production ecological organic fertilier | |
| CN106278752A (en) | A kind of mineral organic fertilizer | |
| CN1357520A (en) | Regularly released granular organic fertilizer and its production process | |
| CN206337182U (en) | Sludge high temperature aerobic fermented manure handles disposal system | |
| CN104496586A (en) | Stacking composting method based on livestock bodies | |
| CN110041151A (en) | A kind of harmless treatment process for waste of breeding silkworms | |
| US20200354284A1 (en) | Preparing organic fertilizer from agricultural wastes and livestock manure | |
| CN106927971A (en) | A kind of sludge soil-repairing agent, preparation method and its application in sludge is dissolved | |
| JP2000169270A (en) | Organic fertilizer and treatment of dehydrated sludge | |
| CN100366586C (en) | Preparation method of organic fertilizer using garbage faeces as raw material | |
| CN214299801U (en) | Combined energy-saving automatic circulation ecological system | |
| CN108675899A (en) | Base manure composite fertilizer and its application | |
| Chadar et al. | Composting as an eco-friendly method to recycle organic waste | |
| CN112898056A (en) | Advanced technology for resource utilization of municipal domestic sludge | |
| CN113526993A (en) | Intelligent control method and system for treating livestock and poultry manure through roller fermentation composting | |
| CN111943472A (en) | Combined energy-saving automatic circulation ecological system and method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CP01 | Change in the name or title of a patent holder | ||
| CP01 | Change in the name or title of a patent holder |
Address after: 830000 Jingshui Road, North District, high tech Zone, Urumqi City, Xinjiang Uygur Autonomous Region Patentee after: Xinjiang tianwu ecological environmental protection Co., Ltd Address before: 830000 Jingshui Road, North District, high tech Zone, Urumqi City, Xinjiang Uygur Autonomous Region Patentee before: Xinjiang tianwu Ecological Technology Co., Ltd |