CN107662914A - Utilize the method and processing system of tunnel cave charing house refuse - Google Patents
Utilize the method and processing system of tunnel cave charing house refuse Download PDFInfo
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- CN107662914A CN107662914A CN201710953559.XA CN201710953559A CN107662914A CN 107662914 A CN107662914 A CN 107662914A CN 201710953559 A CN201710953559 A CN 201710953559A CN 107662914 A CN107662914 A CN 107662914A
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- 238000000034 method Methods 0.000 title claims abstract description 60
- 239000010813 municipal solid waste Substances 0.000 claims abstract description 89
- 230000008569 process Effects 0.000 claims abstract description 26
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 24
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 24
- 238000005056 compaction Methods 0.000 claims abstract description 14
- 239000007789 gas Substances 0.000 claims abstract description 14
- 238000000465 moulding Methods 0.000 claims abstract description 14
- 238000000197 pyrolysis Methods 0.000 claims abstract description 11
- 238000002485 combustion reaction Methods 0.000 claims abstract description 10
- 239000002994 raw material Substances 0.000 claims abstract description 9
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 8
- 230000023556 desulfurization Effects 0.000 claims abstract description 8
- 238000005406 washing Methods 0.000 claims abstract description 7
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 6
- 239000003546 flue gas Substances 0.000 claims abstract description 6
- 238000001816 cooling Methods 0.000 claims description 23
- 239000011449 brick Substances 0.000 claims description 14
- 239000010865 sewage Substances 0.000 claims description 10
- 238000005245 sintering Methods 0.000 claims description 9
- 238000005520 cutting process Methods 0.000 claims description 8
- 230000006835 compression Effects 0.000 claims description 5
- 238000007906 compression Methods 0.000 claims description 5
- 238000001035 drying Methods 0.000 claims description 5
- 238000000605 extraction Methods 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 3
- 238000000746 purification Methods 0.000 claims description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 3
- 238000012856 packing Methods 0.000 claims 1
- 239000000446 fuel Substances 0.000 abstract description 7
- 239000004566 building material Substances 0.000 abstract description 5
- 239000002699 waste material Substances 0.000 description 7
- 230000009467 reduction Effects 0.000 description 4
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 108010022579 ATP dependent 26S protease Proteins 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000003763 carbonization Methods 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 239000003610 charcoal Substances 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 238000004134 energy conservation Methods 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000005457 optimization Methods 0.000 description 2
- 230000000505 pernicious effect Effects 0.000 description 2
- 238000003672 processing method Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000012492 regenerant Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- GQPLMRYTRLFLPF-UHFFFAOYSA-N Nitrous Oxide Chemical class [O-][N+]#N GQPLMRYTRLFLPF-UHFFFAOYSA-N 0.000 description 1
- 238000010000 carbonizing Methods 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000000686 essence Substances 0.000 description 1
- 239000011451 fired brick Substances 0.000 description 1
- 239000002803 fossil fuel Substances 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- 239000003517 fume Substances 0.000 description 1
- 150000002240 furans Chemical class 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 238000003032 molecular docking Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000036301 sexual development Effects 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000012265 solid product Substances 0.000 description 1
- 238000009270 solid waste treatment Methods 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/132—Waste materials; Refuse; Residues
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/60—Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- Dispersion Chemistry (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention provides a kind of method and processing system that house refuse is carbonized using tunnel cave, including refuse classification;Compaction moulding;Charing process, the preheating zone that executing garbage is transported to tunnel cave are dehydrated;The clinkering zone that dried executing garbage is loaded to closed container feeding tunnel cave carries out high temperature pyrolysis burning, realizes that high temperature garbage carbonizes, forms high temperature rubbish carbon block;Cool;Vent gas treatment, desulfurization washing tower purified treatment is transported to by flue through air-introduced machine to flue gas caused by high-temp combustion, realizes qualified discharge.The method provided by the invention that house refuse is carbonized using tunnel cave, house refuse is carbonized using tunnel cave, the raw material of building materials can also be acted on by house refuse had both been may be used as fuel after charing, realize house refuse terminal processes, the utilization rate of house refuse is improved, reduces secondary pollution.
Description
Technical field
The invention belongs to technical field of waste treatment, is to be related to one kind using tunnel cave charing life rubbish more specifically
The method and processing system of rubbish.
Background technology
As the fast development of urbanization and living standards of the people increasingly improve, China's application of city life garbage amount of clearing still exists
Rapid growth, it has also become an important factor for restricting urban sustainable development sexual development.Due to house refuse complicated components, calorific value is low, water
Divide height, secondary pollution can be caused by dealing with improperly.Current Prediction for Solid Waste Treatment Technology mainly has landfill, compost and burning electricity generation etc.
Several ways, but terminal disposal is all difficult to, there is secondary pollution in various degree.House refuse charring process is a kind of
New application technology as the second resource, its product are the solid products rich in carbonaceous and inorganic matter, and both may be used as fuel can also
Act on the raw material of building materials.But the equipment of its key equipment retort still lacks industrialized application.
The content of the invention
It is an object of the invention to provide a kind of method that house refuse is carbonized using tunnel cave, using tunnel cave to life
Rubbish is carbonized, and the raw material of building materials can also be acted on by house refuse had both been may be used as fuel after charing, realize life rubbish
Rubbish terminal processes, the utilization rate of house refuse is improved, reduce secondary pollution.
To achieve the above object, the technical solution adopted by the present invention is:One kind is provided using tunnel cave charing house refuse
Method, comprise the following steps:
Refuse classification:Sorting classification is carried out to house refuse, is divided into Recyclable and expendable house refuse, pair can
Regenerant is reclaimed;
Compaction moulding:Expendable house refuse feeding compressing baling press is compressed, extrudes the air in rubbish
And sewage, and with cutting into several executing garbages;
Charing process:The preheating zone that executing garbage is transported to tunnel cave is dehydrated;Dried executing garbage is led to
Cross manipulator and load the clinkering zone progress high temperature pyrolysis burning that closed container is sent into tunnel cave, realize that high temperature garbage carbonizes, formed
High temperature rubbish carbon block;
Cool:High temperature executing garbage after charing is sent into the cooling zone cooling down of tunnel cave, after cooling down
Rubbish carbon block is sent out from kiln tail;
Vent gas treatment:Flue gas caused by high-temp combustion is transported to desulfurization washing tower purified treatment through air-introduced machine by flue,
Realize qualified discharge.
Further, in the compaction moulding, the sewage collecting squeezed out to sewage accumulator tank is carried out at precipitation purification
Reason, as secondary use.
Further, in the clinkering zone of the charing process, high temperature caused by the executing garbage high temperature pyrolysis in closed container
Gas is used as auxiliary air feeding clinkering zone through pipeline by air-introduced machine extraction and is used as roasting combustion-supporting.
Further, in the clinkering zone of the charing process, burning zone temperature is between 800-1000 DEG C.
Further, in the clinkering zone of the charing process, the executing garbage high temperature pyrolysis time control in closed container exists
1-1.5 hour.
Further, in the preheating zone of the charing process, the drying and dehydrating time is 0.5-1 hours.
Further, described to cool, cooling zone cool time was controlled in 1-2 hours.
Further, described to cool, rubbish carbon block outlet temperature is 70-80 DEG C.
Further, described to cool, the rubbish carbon block after cooling treatment is after crushing as sintering wall body brick
Raw material.
The beneficial effect of the method provided by the invention that house refuse is carbonized using tunnel cave is:With prior art phase
Than the present invention passes through classification recovery, compaction moulding, brickkiln charcoal using the method for tunnel cave charing house refuse by that will live
Change, carbon block is made, as the internal combustion of sintering wall body brick, the expendable rubbish of one side recycles again, realizes house refuse
Cmpletely recycle, reduce secondary pollution;On the other hand the land use of landfill disposed waste is reduced, shoveling of fetching earth is reduced and makes
Into land destruction, for Energy-saving Tunnel Kiln consumption reduction, optimization garbage as resource disposal it is significant.
The present invention is carbonized using tunnel cave to rubbish, and due to the 26S Proteasome Structure and Function of tunnel cave, executing garbage is at each section
Temperature and the residence time it is different, from preheating zone, burn till and take the processing of cooling zone to, by the way that house refuse is carbonized, become rich
Carbon block containing carbonaceous and inorganic matter, realize it is energy-saving, with waste incinerator handle rubbish compared with, fractional energy savings below 120%,
Compared with traditional garbage loading embeading mode, Economization on land.
The present invention also provides a kind of domestic garbage treating system, including the rubbish for being sorted to house refuse is located in advance
Manage unit, the compressing baling press for carrying out compaction moulding to expendable house refuse, for the rubbish progress to compacting
The cutting machine of cutting, the tunnel cave for carrying out charing process to executing garbage and the desulfurization for carrying out purified treatment to tail gas are washed
Wash tower.
The beneficial effect of domestic garbage treating system provided by the invention is:System provided by the invention, being capable of rubbish
Classified, charing process is carried out to expendable rubbish, the executing garbage of charing can be used for wall raw material, reduce discarded object
Yield, reach the purpose of twice laid.
Brief description of the drawings
Technical scheme in order to illustrate the embodiments of the present invention more clearly, below will be to embodiment or description of the prior art
In the required accompanying drawing used be briefly described, it should be apparent that, drawings in the following description be only the present invention some
Embodiment, for those of ordinary skill in the art, without having to pay creative labor, can also be according to these
Accompanying drawing obtains other accompanying drawings.
Fig. 1 is the process chart of the method provided in an embodiment of the present invention that house refuse is carbonized using tunnel cave;
Fig. 2 is the structural representation provided in an embodiment of the present invention that domestic garbage treating system is carbonized using tunnel cave.
Embodiment
In order that technical problems, technical solutions and advantages to be solved are more clearly understood, tie below
Drawings and Examples are closed, the present invention will be described in further detail.It should be appreciated that specific embodiment described herein is only
To explain the present invention, it is not intended to limit the present invention.
It should be noted that when element is referred to as " being fixed on " or " being arranged at " another element, it can be directly another
On one element or it is connected on another element.When an element is known as " being connected to " another element, it can
To be directly to another element or be indirectly connected on another element.
It is to be appreciated that term " length ", " width ", " on ", " under ", "front", "rear", "left", "right", " vertical ",
The orientation or position relationship of the instruction such as " level ", " top ", " bottom " " interior ", " outer " are to be closed based on orientation shown in the drawings or position
System, it is for only for ease of and describes the present invention and simplify description, rather than indicates or imply that signified device or element must have
Specific orientation, with specific azimuth configuration and operation, therefore be not considered as limiting the invention.
Also referring to Fig. 1 and Fig. 2, now the method provided by the invention that house refuse is carbonized using tunnel cave is said
It is bright.The method that house refuse is carbonized using tunnel cave, is comprised the following steps:
Refuse classification:Sorting classification is carried out to house refuse, is divided into Recyclable and expendable house refuse, pair can
Regenerant is reclaimed;
Compaction moulding:Expendable house refuse feeding compressing baling press is compressed, extrudes the air in rubbish
And sewage, and with cutting into several executing garbages;
Charing process:The preheating zone that executing garbage is transported to tunnel cave is dehydrated;Dried executing garbage is led to
Cross manipulator and load the clinkering zone progress high temperature pyrolysis burning that closed container is sent into tunnel cave, realize that high temperature garbage carbonizes, formed
High temperature rubbish carbon block;
Cool:High temperature executing garbage after charing is sent into the cooling zone cooling down of tunnel cave, after cooling down
Rubbish carbon block is sent out from kiln tail;
Vent gas treatment:Flue gas caused by high-temp combustion is transported to desulfurization washing tower purified treatment through air-introduced machine by flue,
Realize qualified discharge.
The method provided by the invention that house refuse is carbonized using tunnel cave, compared with prior art, utilizes tunnel cave pair
The not recyclable rubbish of compaction moulding is carbonized, and prepares New wall brick internal combustion.Especially with existing manufacture novel wall
High-efficiency tunnel kiln used in brick, fuel and flue gas by the use of after carbonizing house refuse as tunnel cave fuel, as burning
The internal combustion of New wall brick is tied, reaches and reduces denitration cost, coal consumption is saved, reduce discharged nitrous oxides and locates useless multiple effect
Fruit.
Sintered brick and tile industry is the important industry of China's building material.Tunnel cave is the main burning of fired brick industry class Large-scale enterprises
Forming apparatus, fossil fuel are mainly used in sintering and dried.Tunnel cave is made up of preheating zone, clinkering zone, cooling zone three parts, is passed through
Kiln car conveys in tunnel.It is different with the residence time in each section of temperature due to the special 26S Proteasome Structure and Function of tunnel cave, can
For disposing discarded object, realize energy-saving.By the way that house refuse is carbonized, become the carbon block rich in carbonaceous and inorganic matter,
Can be with the internal combustion together with the material used in New wall brick after broken as sintering New wall brick.
Life refuse processing method provided by the invention, charcoal is carried out to the not recyclable rubbish of compaction moulding using tunnel cave
Change, can thoroughly destroy the dioxin in rubbish by fire.Rubbish carbon block can realize that crude fuel substitutes, and carbonaceous and nothing are comprised only in rubbish carbon block
Machine thing;Rubbish carbon block is burnt till, convenience in transport is also used as other building materials, and industry energy-saving consumption reduction is obvious.At relevant rubbish
Manage energy consumption index to calculate, rubbish charing process energy consumption is usually 4.1-5kw/T, compares incinerator as handled 80,000 tons of house refuses year
The house refuse of phase homogenous quantities, annual to save equivalent 6600 tons of coal of mark, tunnel cave charing process is compared with waste incinerator, section
Energy rate is more than 120%;Compared with traditional garbage loading embeading mode, Economization on land.
This method includes the complete techniques such as sorting consumer waste, compaction moulding, brickkiln charing, exhaust-gas treatment.Technique stream
Journey is simple, and equipment is production domesticization, and cheap, equipment investment cost is low, and can realize seamless with conventional garbage treatment plant
Docking.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, in the compaction moulding, the sewage collecting squeezed out to sewage accumulator tank is subjected to precipitation purification processing, made
For secondary use.Waste water after processing, can be transported to brickmaking mixer and clay brick, watering greening, sprinkling ground, cleaning are set
It is standby to wait multiple use, the utilization of pure water is reduced, energy-conserving and environment-protective.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, in the clinkering zone of the charing process, high-temperature gas caused by the executing garbage high temperature pyrolysis in closed container
Being used as auxiliary air feeding clinkering zone through pipeline by air-introduced machine extraction is used as roasting combustion-supporting.It is pyrolyzed a part of conduct of high-temperature hot-air
Auxiliary air by kiln wall air outlet be sent into clinkering zone be used as roasting it is combustion-supporting, reach save fuel, raw material emission reduction energy-conservation and locate
Useless resultant effect.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, in the clinkering zone of the charing process, burning zone temperature is between 800-1000 DEG C.Due to burning zone temperature
At 1000 DEG C or so, the time in 1-2 hours, can fully destroy dioxin by fire.
Further, refering to Fig. 1, a kind of as the method provided by the invention that house refuse is carbonized using tunnel cave is had
Body embodiment, in the clinkering zone of the charing process, the executing garbage high temperature pyrolysis time control in closed container is small in 1-1.5
When.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, in the preheating zone of the charing process, the drying and dehydrating time is 0.5-1 hours.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, described to cool, cooling zone cool time was controlled in 1-2 hours.
Further, refering to Fig. 1, a kind of as the method provided by the invention that house refuse is carbonized using tunnel cave is had
Body embodiment, described to cool, rubbish carbon block outlet temperature is 70-80 DEG C.
Further, referring to Fig. 1, as it is provided by the invention using tunnel cave carbonize house refuse method one kind
Embodiment, described to cool, rubbish carbon block after the cooling treatment raw material as sintering wall body brick after crushing.
As a specific embodiment, make complete narration to life refuse processing method provided by the invention below:
After municipal house refuse is sorted, the Recyclables such as building waste, metal class are filtered out, by special compressing baling press, are passed through
100 tons of vertical compression baling press compression, suppresses 3-5 times, the air in rubbish and moisture is extruded, are made repeatedly
1600mmx1850mmx1400mm (the long wide x of x are high) executing garbage, certainly, executing garbage can carry out size cutting according to practical application.
Kiln car (namely bake bricks car) of the executing garbage made through tunnel cave is dehydrated from kiln hood into preheating zone, will be dried
Executing garbage loads closed container by manipulator, and being sent into clinkering zone by kiln car carries out high temperature cabonization, can be by controlling clinkering zone
Temperature realizes that the anoxic of executing garbage in closed container thermally decomposes within 800-1000 DEG C, Volatile pernicious gas, finally
Realize charing.The pernicious gases such as the dioxin that discharges, furans are thoroughly destroyed by fire by high-temp combustion twice, are passed through by air-introduced machine
Flue is transported to desulfurization washing tower purified treatment, realizes qualified discharge.High temperature carbon block after charing enter after cooling zone cooling from
Kiln tail is sent out.Cooling zone is blasted outdoor air by air blower, and the hot blast part after heat exchange passes through kiln wall as auxiliary air
Air outlet is sent into clinkering zone and is used as roasting combustion-supporting, reaches and saves the resultant effect that fuel, the emission reduction energy-conservation of raw material and place give up.
Wherein, executing garbage is sent into preheating zone from kiln hood to be dried, drying time in 0.5-1 hours, then by drying
Rear executing garbage loads closed container, and being sent into clinkering zone by car of baking bricks carries out high temperature pyrolysis, temperature control at 800-1000 DEG C, when
Between control heating rate can be by main valve control of discharging fume within 1-1.5 hours, kiln, total valve opening reduces, and negative pressure draft is small, heating
Speed is reduced.Rubbish carbon block after carbonization enters cooling zone cooling about 1-2 hours, according to chilling temperature regulating time, carbon block
About 70-80 DEG C of outlet temperature.Internal combustion of the carbon block after broken as sintering New wall brick after cooling.
Referring to Fig. 2, the present invention, which also provides a kind of present invention, also provides a kind of domestic garbage treating system, including for pair
The rubbish pretreatment unit that house refuse is sorted, the compression for carrying out compaction moulding to expendable house refuse are beaten
Chartered plane, for the rubbish of compacting is cut cutting machine, for executing garbage carry out charing process tunnel cave and be used for
The desulfurization washing tower of purified treatment is carried out to tail gas.
Further, referring to Fig. 2, the present invention, which also provides a kind of present invention, also provides a kind of domestic garbage treating system,
The sewage accumulator tank that also includes being used to handle moisture content at compressed baling press compression, the connection closed container and described burn till
Band is used to hot blast introducing the air-introduced machine of the sintering zone of tunnel furnace, the disintegrating machine for crushing the rubbish carbon block.
Wherein, throughout between science and engineering sequence, for solid refuse, can be conveyed using conveyer belt, for waste water and gas,
Conveyed by closed conduit, reduce and surrounding environment is polluted, while to realize the purpose to save land, set between each operation
Put rationally compact, to reduce and take up an area and the resource of each link can be recycled and is advisable in layout.
Domestic garbage treating system provided by the invention, to Waste sorting recycle, expendable house refuse is carried out
Compaction moulding, sintering carbonization, consider sewage recycling processing, high-temperature flue gas recycling processing and gas cleaning processing
Deng realizing energy-saving and emission-reduction to greatest extent, reduce secondary pollution, energy-saving, the consumption of Economization on land and the energy, for tunnel
Kiln is energy-saving and optimization garbage as resource disposal is significant.
The foregoing is merely illustrative of the preferred embodiments of the present invention, is not intended to limit the invention, all essences in the present invention
All any modification, equivalent and improvement made within refreshing and principle etc., should be included in the scope of the protection.
Claims (10)
1. utilize the method for tunnel cave charing house refuse, it is characterised in that comprise the following steps:
Refuse classification:Sorting classification is carried out to house refuse, is divided into Recyclable and expendable house refuse, to recyclable
Thing is reclaimed;
Compaction moulding:Expendable house refuse feeding compressing baling press is compressed, extrudes the air in rubbish and dirt
Water, and with cutting into several executing garbages;
Charing process:The preheating zone that executing garbage is transported to tunnel cave is dehydrated;Dried executing garbage is passed through into machine
Tool hand loads the clinkering zone progress high temperature pyrolysis burning that closed container is sent into tunnel cave, realizes that high temperature garbage carbonizes, forms high temperature
Rubbish carbon block;
Cool:High temperature executing garbage after charing is sent into the cooling zone cooling down of tunnel cave, the rubbish after cooling down
Carbon block is sent out from kiln tail;
Vent gas treatment:Flue gas caused by high-temp combustion is transported to desulfurization washing tower purified treatment through air-introduced machine by flue, realizes
Qualified discharge.
2. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:The compaction moulding
In, the sewage collecting squeezed out to sewage accumulator tank is subjected to precipitation purification processing, as secondary use.
3. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:The charing process
In clinkering zone, high-temperature gas caused by the executing garbage high temperature pyrolysis in closed container is used as secondary by air-introduced machine extraction through pipeline
It is combustion-supporting as being calcined that air is sent into clinkering zone.
4. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:The charing process
In clinkering zone, burning zone temperature is between 800-1000 DEG C.
5. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:The charing process
In clinkering zone, the executing garbage high temperature pyrolysis time control in closed container is in 1-1.5 hours.
6. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:The charing process
In preheating zone, the drying and dehydrating time is 0.5-1 hours.
7. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:It is described to cool
In, cooling zone cool time was controlled in 1-2 hours.
8. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:It is described to cool
In, rubbish carbon block outlet temperature is 70-80 DEG C.
9. the method for tunnel cave charing house refuse is utilized as claimed in claim 1, it is characterised in that:It is described to cool
In, the rubbish carbon block after cooling treatment is after crushing as the raw material for sintering wall body brick.
10. the domestic garbage treating system that method as claimed in any one of claims 1-9 wherein uses, it is characterised in that:Including
For house refuse is sorted rubbish pretreatment unit, for being compressed packing to expendable house refuse
Compressing baling press, the cutting machine for being cut to the rubbish of compression, the tunnel cave for carrying out charing process to executing garbage
With the desulfurization washing tower for carrying out purified treatment to tail gas.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109028075A (en) * | 2018-06-01 | 2018-12-18 | 陕西志清宇泰环保设备有限公司 | A kind of refuse pyrolysis treatment process |
CN109990607A (en) * | 2018-11-28 | 2019-07-09 | 葛小方 | A kind of tunnel kiln waste gas treatment system and treatment method |
Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4017921A1 (en) * | 1989-06-07 | 1991-12-12 | Nieberding Jean Louis | Tunnel furnace giving effective redn. of rubbish - consisting of trolleys to carry refuse and expanding gas transferred to burner |
US6006682A (en) * | 1998-02-09 | 1999-12-28 | Hung; Ming-Chin | Garbage incinerator with tunnel furnace combustion |
EP1156275A1 (en) * | 2000-05-12 | 2001-11-21 | Kun-Cheng Wu | Refuse incinerating oven |
CN1459585A (en) * | 2002-05-22 | 2003-12-03 | 欧书信 | Pollutionless garbage burning method of heat carrying circulation tunnel kiln |
CN1644492A (en) * | 2004-12-10 | 2005-07-27 | 彭立军 | Charcoal production from house refuse |
CN101367086A (en) * | 2007-07-25 | 2009-02-18 | 练其辉 | Disposal method for thorough recycling of solid waste |
CN101519300A (en) * | 2008-02-27 | 2009-09-02 | 李兴业 | Method for manufacturing bricks by using household garbage |
CN102878568A (en) * | 2012-11-05 | 2013-01-16 | 刘贡友 | Tunnel type kiln and method for multi-temperature-gradation photon energy waste incineration treatment |
CN103322574A (en) * | 2012-03-21 | 2013-09-25 | 四川国立能源科技有限公司 | Method for co-processing household garbage by using tunnel kiln sintered brick production line and processing system thereof |
CN204234452U (en) * | 2014-08-02 | 2015-04-01 | 梅广勇 | Consumer waste incineration complete set of equipments |
-
2017
- 2017-10-13 CN CN201710953559.XA patent/CN107662914B/en active Active
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4017921A1 (en) * | 1989-06-07 | 1991-12-12 | Nieberding Jean Louis | Tunnel furnace giving effective redn. of rubbish - consisting of trolleys to carry refuse and expanding gas transferred to burner |
US6006682A (en) * | 1998-02-09 | 1999-12-28 | Hung; Ming-Chin | Garbage incinerator with tunnel furnace combustion |
EP1156275A1 (en) * | 2000-05-12 | 2001-11-21 | Kun-Cheng Wu | Refuse incinerating oven |
CN1459585A (en) * | 2002-05-22 | 2003-12-03 | 欧书信 | Pollutionless garbage burning method of heat carrying circulation tunnel kiln |
CN1644492A (en) * | 2004-12-10 | 2005-07-27 | 彭立军 | Charcoal production from house refuse |
CN101367086A (en) * | 2007-07-25 | 2009-02-18 | 练其辉 | Disposal method for thorough recycling of solid waste |
CN101519300A (en) * | 2008-02-27 | 2009-09-02 | 李兴业 | Method for manufacturing bricks by using household garbage |
CN103322574A (en) * | 2012-03-21 | 2013-09-25 | 四川国立能源科技有限公司 | Method for co-processing household garbage by using tunnel kiln sintered brick production line and processing system thereof |
CN102878568A (en) * | 2012-11-05 | 2013-01-16 | 刘贡友 | Tunnel type kiln and method for multi-temperature-gradation photon energy waste incineration treatment |
CN204234452U (en) * | 2014-08-02 | 2015-04-01 | 梅广勇 | Consumer waste incineration complete set of equipments |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109028075A (en) * | 2018-06-01 | 2018-12-18 | 陕西志清宇泰环保设备有限公司 | A kind of refuse pyrolysis treatment process |
CN109990607A (en) * | 2018-11-28 | 2019-07-09 | 葛小方 | A kind of tunnel kiln waste gas treatment system and treatment method |
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