CN106077024A - Process the system and method for house refuse - Google Patents
Process the system and method for house refuse Download PDFInfo
- Publication number
- CN106077024A CN106077024A CN201610430277.7A CN201610430277A CN106077024A CN 106077024 A CN106077024 A CN 106077024A CN 201610430277 A CN201610430277 A CN 201610430277A CN 106077024 A CN106077024 A CN 106077024A
- Authority
- CN
- China
- Prior art keywords
- outlet
- gas
- pyrolysis
- entrance
- cement
- 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.)
- Pending
Links
- 238000000034 method Methods 0.000 title claims abstract description 107
- 230000008569 process Effects 0.000 title claims description 72
- 238000000197 pyrolysis Methods 0.000 claims abstract description 139
- 239000004568 cement Substances 0.000 claims abstract description 136
- 239000007789 gas Substances 0.000 claims abstract description 131
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 64
- 230000002195 synergetic effect Effects 0.000 claims abstract description 58
- 238000009825 accumulation Methods 0.000 claims abstract description 45
- 239000002296 pyrolytic carbon Substances 0.000 claims abstract description 43
- 239000002994 raw material Substances 0.000 claims abstract description 39
- 239000010815 organic waste Substances 0.000 claims abstract description 37
- 239000000446 fuel Substances 0.000 claims abstract description 36
- 235000012255 calcium oxide Nutrition 0.000 claims abstract description 30
- 239000000292 calcium oxide Substances 0.000 claims abstract description 30
- 239000002912 waste gas Substances 0.000 claims abstract description 17
- 238000002485 combustion reaction Methods 0.000 claims abstract description 10
- 239000010813 municipal solid waste Substances 0.000 claims description 51
- 239000010865 sewage Substances 0.000 claims description 39
- 238000000926 separation method Methods 0.000 claims description 19
- 238000000227 grinding Methods 0.000 claims description 15
- 239000002002 slurry Substances 0.000 claims description 11
- 238000003860 storage Methods 0.000 claims description 9
- 239000012530 fluid Substances 0.000 claims description 7
- 238000002955 isolation Methods 0.000 claims description 6
- 239000000567 combustion gas Substances 0.000 claims description 5
- 238000004519 manufacturing process Methods 0.000 abstract description 24
- 230000008901 benefit Effects 0.000 abstract description 10
- 238000004064 recycling Methods 0.000 abstract description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 21
- 239000000463 material Substances 0.000 description 20
- 238000006243 chemical reaction Methods 0.000 description 12
- 239000004567 concrete Substances 0.000 description 10
- 238000010586 diagram Methods 0.000 description 9
- 238000007233 catalytic pyrolysis Methods 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 8
- 239000004927 clay Substances 0.000 description 7
- 239000011269 tar Substances 0.000 description 7
- 235000019738 Limestone Nutrition 0.000 description 6
- 239000006028 limestone Substances 0.000 description 6
- 238000011068 loading method Methods 0.000 description 6
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 6
- 230000001698 pyrogenic effect Effects 0.000 description 6
- 238000001816 cooling Methods 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 239000003245 coal Substances 0.000 description 4
- 238000005265 energy consumption Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 241000219422 Urtica Species 0.000 description 3
- 235000009108 Urtica dioica Nutrition 0.000 description 3
- 239000011449 brick Substances 0.000 description 3
- 239000003610 charcoal Substances 0.000 description 3
- 239000003034 coal gas Substances 0.000 description 3
- 239000000356 contaminant Substances 0.000 description 3
- 238000006477 desulfuration reaction Methods 0.000 description 3
- 230000023556 desulfurization Effects 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 239000011521 glass Substances 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 239000012716 precipitator Substances 0.000 description 3
- 238000007873 sieving Methods 0.000 description 3
- 238000009827 uniform distribution Methods 0.000 description 3
- 241000196324 Embryophyta Species 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 230000002073 mitogenetic effect Effects 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- 239000002918 waste heat Substances 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 238000005276 aerator Methods 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 231100000584 environmental toxicity Toxicity 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 239000011286 gas tar Substances 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000007096 poisonous effect Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 210000000952 spleen Anatomy 0.000 description 1
- 238000004148 unit process Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- 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
- C04B7/00—Hydraulic cements
- C04B7/24—Cements from oil shales, residues or waste other than slag
-
- 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
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
Abstract
The invention discloses the system and method processing house refuse, this system includes: pretreatment unit, and pretreatment unit has house refuse entrance, foul smell outlet, organic waste outlet, inorganic refuse outlet and the first outlet of sewer;Heat accumulation type radiant tube revolving bed, heat accumulation type radiant tube revolving bed has the first combustible gas entrance, combustion air inlet, quick lime entrance, organic waste entrance, pyrolysis oil gas vent and pyrolytic carbon outlet, combustion air inlet is connected with foul smell outlet, and organic waste entrance is connected with organic waste outlet;Cement kiln synergetic unit, cement kiln synergetic unit has feed(raw material)inlet, fuel inlet, waste gas outlet and cement exit, and feed(raw material)inlet is connected with inorganic refuse outlet, and fuel inlet is connected with pyrolytic carbon outlet.This system is possible not only to effectively reduce manufacture of cement cost, and can realize the innoxious of house refuse and recycling treatment, has huge economic benefit and social benefit.
Description
Technical field
The invention belongs to chemical technology field, specifically, the present invention relates to a kind of system processing house refuse and side
Method.
Background technology
At present, the process problem of domestic waste becomes whole people's focus of attention already.Existing landfill, compost, burning
Etc. technology due to himself intrinsic shortcoming so that it is development is limited to.China many urban construction consumer waste incineration is sent out
Power plant, but burn the two English pollution problems brought and cause people's dispute to waste incineration mode.Two English environmental toxicities
Greatly, the most degradable, cause great threat to resident is healthy.The method using cement kiln synergic processing rubbish, existing skill
Art have rubbish is directly burned after or directly garbage raw material is thrown away in cement kiln.Directly burn away the refuse and can produce two English etc.
Pollute environment, produce the device of some corrosive gas meeting corrosive water stall, breaking plant;And directly house refuse is thrown away into water
Reacting in stall, the complicated component of rubbish, water content high can affect the quality of cement products, affects whole cement kiln
Technique.
Therefore, the technology of existing process house refuse is further improved.
Summary of the invention
It is contemplated that one of technical problem solved the most to a certain extent in correlation technique.To this end, the present invention
One purpose is to propose a kind of system and method processing house refuse, and this system is by by the process of house refuse and cement
Kiln is worked in coordination with treatment technology and is combined, and is possible not only to effectively reduce manufacture of cement cost, and can realize house refuse
Innoxious and recycling treatment, there is huge economic benefit and social benefit.
In the first aspect of the invention, this present invention proposes a kind of system processing house refuse.According to the present invention
Embodiment, this system includes:
Pretreatment unit, described pretreatment unit have house refuse entrance, foul smell outlet, organic waste outlet, inorganic
Garbage outlet and the first outlet of sewer;
Heat accumulation type radiant tube revolving bed, described heat accumulation type radiant tube revolving bed has the first combustible gas entrance, combustion air
Entrance, quick lime entrance, organic waste entrance, pyrolysis oil gas vent and pyrolytic carbon outlet, described combustion air inlet is with described
Foul smell outlet is connected, and described organic waste entrance is connected with the outlet of described organic waste;
Cement kiln synergetic unit, described cement kiln synergetic unit has feed(raw material)inlet, fuel inlet, waste gas go out
Mouth and cement exit, described feed(raw material)inlet is connected with the outlet of described inorganic refuse, and described fuel inlet exports with described pyrolytic carbon
It is connected.
Thus, the system of process house refuse according to embodiments of the present invention is by obtaining after house refuse pretreatment
Organic waste, foul smell and the supply of cement raw material quick lime carry out pyrolysis processing, quick lime to heat accumulation type radiant tube revolving bed
Can be with the pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this portion
Mitogenetic Calx can supply after pyrogenic processes to subsequent process and use as cement producting material, thus is processed into not increasing
The wasting of resources that garbage loading embeading or burning cause can be avoided while Ben, and can effectively solve to burn by pyrolysis processing
The problem that two English that rubbish is brought pollute, supplies gained pyrolytic carbon to cement kiln synergetic unit as combustion simultaneously
Material uses, and will coordinate limestone, clay matter etc. in pretreatment unit gained inorganic refuse supply to cement kiln synergetic unit
As cement slurry, so it is possible not only to effectively reduce cement cost, and so that separating obtained inorganic refuse is filled
Divide and utilize, such that it is able to garbage disposal is combined with cement kiln synergetic unit, relative to existing cement kiln
Cooperative disposal method, in this application, once cement kiln production line stops production, and house refuse can also be pyrolyzed in advance, will not bank up
Smelly, produce the problem that rubbish can be put nowhere, thus realize the innoxious of house refuse and recycling treatment.
It addition, the system of process house refuse according to the above embodiment of the present invention can also have following additional technology
Feature:
In some embodiments of the invention, the system of described process house refuse farther includes: Oil-gas Separation purifies
Device, described Oil-gas Separation purifier has pyrolysis oil gas entrance, pyrolysis gas outlet, pyrolysis oil outlet and the second sewage and goes out
Mouthful, described pyrolysis oil gas entrance is connected with described pyrolysis oil gas vent, and the outlet of described pyrolysis oil is connected with described fuel inlet;Can
Combustion gas storage tank, described combustible gas storage tank has the second combustible gas entrance and the outlet of the second combustible gas, described second combustible gas entrance
Being connected with described pyrolysis gas outlet, described second combustible gas outlet is connected with described first combustible gas entrance;Sewage-treatment plant,
Described sewage-treatment plant have sewage inlet and treatment fluid outlet, described sewage inlet respectively with described first outlet of sewer and
Described second outlet of sewer is connected.Thus, it is possible to significantly improve the environmental benefit of this system.
In some embodiments of the invention, the outlet of described pyrolytic carbon and the preheating in described cement kiln synergetic unit
Device, dore furnace are connected with the fuel inlet at least one in rotary kiln.Thus, it is possible to significantly reduce manufacture of cement cost.
In some embodiments of the invention, the outlet of described pyrolysis oil and the preheating in described cement kiln synergetic unit
Device, dore furnace are connected with the fuel inlet at least one in rotary kiln.Become thus, it is possible to reduce manufacture of cement further
This.
In some embodiments of the invention, the system of described process house refuse farther includes: TRT, described
TRT has exhaust gas entrance and the outlet of boiler residual air, and described exhaust gas entrance is connected with described waste gas outlet, described boiler residual
Gas outlet is connected with the raw material grinding mill in described cement kiln synergetic unit.Thus, it is possible to significantly reduce system energy consumption.
In another aspect of the invention, the present invention proposes a kind of method processing house refuse.According to the present invention's
Embodiment, the method is that the system using process house refuse described above is carried out.According to a particular embodiment of the invention,
The method includes:
(1) will house refuse supply to described pretreatment unit carries out pretreatment, in order to obtain foul smell, organic waste,
Inorganic refuse and the first sewage;
(2) by the supply of quick lime, described organic waste and described foul smell to described heat accumulation type radiant tube revolving bed, in order to right
Described organic waste carries out pyrolysis processing, obtains being pyrolyzed oil gas and pyrolytic carbon;
(3) described inorganic refuse and described pyrolytic carbon are supplied extremely described cement kiln synergetic unit and make described inorganic
Rubbish and cement slurry carry out collaborative process, in order to obtain waste gas and cement.
Thus, the method for process house refuse according to embodiments of the present invention is by obtaining after house refuse pretreatment
Organic waste, foul smell and the supply of cement raw material quick lime carry out pyrolysis processing, quick lime to heat accumulation type radiant tube revolving bed
Can be with the pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this portion
Mitogenetic Calx can supply after pyrogenic processes to subsequent process and use as cement producting material, thus is processed into not increasing
The wasting of resources that garbage loading embeading or burning cause can be avoided while Ben, and can effectively solve to burn by pyrolysis processing
The problem that two English that rubbish is brought pollute, supplies gained pyrolytic carbon to cement kiln synergetic unit as combustion simultaneously
Material uses, and will coordinate limestone, clay matter etc. in pretreatment unit gained inorganic refuse supply to cement kiln synergetic unit
As cement slurry, so it is possible not only to effectively reduce cement cost, and so that separating obtained inorganic refuse is filled
Divide and utilize, such that it is able to garbage disposal is combined with cement kiln synergetic unit, relative to existing cement kiln
Cooperative disposal method, in this application, once cement kiln production line stops production, and house refuse can also be pyrolyzed in advance, will not bank up
Smelly, produce the problem that rubbish can be put nowhere, thus realize the innoxious of house refuse and recycling treatment.
It addition, the method for process house refuse according to the above embodiment of the present invention can also have following additional technology
Feature:
In some embodiments of the invention, the method for described process house refuse farther includes: (4) are by described pyrolysis
Oil gas supply carries out isolation of purified process to described Oil-gas Separation purifier, in order to obtain pyrolysis gas, pyrolysis oil and second dirty
Water, and the supply of described pyrolysis gas is used to described heat accumulation type radiant tube revolving bed as combustion gas, described pyrolysis oil is supplied extremely
Described cement kiln synergetic unit uses as fuel;(5) described first sewage step (1) obtained and step (4) obtain
Described second sewage arrived supplies to sewage-treatment plant, in order to obtain treatment fluid.Thus, it is possible to significantly improve the ring of this system
Protect benefit.
In some embodiments of the invention, described pyrolytic carbon supply step (2) obtained is worked in coordination with to described cement kiln
At least one in preheater, dore furnace and rotary kiln on processing unit uses as fuel.Thus, it is possible to significantly reduce water
Mud production cost.
In some embodiments of the invention, described pyrolysis oil supply step (4) obtained is worked in coordination with to described cement kiln
At least one in preheater, dore furnace and rotary kiln on processing unit uses as fuel.Thus, it is possible to reduce further
Manufacture of cement cost.
In some embodiments of the invention, the method for described process house refuse farther includes: (6) are by step (3)
The described waste gas supply obtained carries out UTILIZATION OF VESIDUAL HEAT IN to described TRT, in order to obtain boiler residual air, and by described boiler residual
Gas supply uses to the raw material grinding mill in described cement kiln synergetic unit as dry medium.Thus, it is possible to significantly reduce it is
System energy consumption.
The additional aspect of the present invention and advantage will part be given in the following description, and part will become from the following description
Obtain substantially, or recognized by the practice of the present invention.
Accompanying drawing explanation
Above-mentioned and/or the additional aspect of the present invention and advantage are from combining the accompanying drawings below description to embodiment and will become
Substantially with easy to understand, wherein:
Fig. 1 is the system structure schematic diagram processing house refuse according to an embodiment of the invention;
Fig. 2 is the system structure schematic diagram of the process house refuse according to further embodiment of the present invention;
Fig. 3 is the system structure schematic diagram of the process house refuse according to another embodiment of the present invention;
Fig. 4 is the system structure schematic diagram of the process house refuse according to another embodiment of the present invention;
Fig. 5 is the system structure schematic diagram of the process house refuse according to another embodiment of the present invention;
Fig. 6 is the method flow schematic diagram processing house refuse according to an embodiment of the invention;
Fig. 7 is the method flow schematic diagram of the process house refuse according to further embodiment of the present invention;
Fig. 8 is the method flow schematic diagram of the process house refuse according to another embodiment of the present invention;
Fig. 9 is the system structure schematic diagram of the process house refuse according to another embodiment of the present invention.
Detailed description of the invention
Embodiments of the invention are described below in detail, and the example of described embodiment is shown in the drawings, the most from start to finish
Same or similar label represents same or similar element or has the element of same or like function.Below with reference to attached
The embodiment that figure describes is exemplary, it is intended to is used for explaining the present invention, and is not considered as limiting the invention.
In describing the invention, it is to be understood that term " " center ", " longitudinally ", " laterally ", " length ", " width ",
" thickness ", " on ", D score, "front", "rear", "left", "right", " vertically ", " level ", " top ", " end ", " interior ", " outward ", " up time
Pin ", " counterclockwise ", " axially ", " radially ", the orientation of the instruction such as " circumferential " or position relationship be based on orientation shown in the drawings or
Position relationship, is for only for ease of the description present invention and simplifies description rather than instruction or imply that the device of indication or element must
Must have specific orientation, with specific azimuth configuration and operation, be therefore not considered as limiting the invention.
Additionally, term " first ", " second " are only used for describing purpose, and it is not intended that instruction or hint relative importance
Or the implicit quantity indicating indicated technical characteristic.Thus, define " first ", the feature of " second " can express or
Implicitly include at least one this feature.In describing the invention, " multiple " are meant that at least two, such as two, three
Individual etc., unless otherwise expressly limited specifically.
In the present invention, unless otherwise clearly defined and limited, term " install ", " being connected ", " connection ", " fixing " etc.
Term should be interpreted broadly, and connects for example, it may be fixing, it is also possible to be to removably connect, or integral;Can be that machinery connects
Connect, it is also possible to be electrical connection;Can be to be joined directly together, it is also possible to be indirectly connected to by intermediary, in can being two elements
The connection in portion or the interaction relationship of two elements, unless otherwise clear and definite restriction.For those of ordinary skill in the art
For, above-mentioned term concrete meaning in the present invention can be understood as the case may be.
In the present invention, unless otherwise clearly defined and limited, fisrt feature second feature " on " or D score permissible
It is that the first and second features directly contact, or the first and second features are by intermediary mediate contact.And, fisrt feature exists
Second feature " on ", " top " and " above " but fisrt feature directly over second feature or oblique upper, or be merely representative of
Fisrt feature level height is higher than second feature.Fisrt feature second feature " under ", " lower section " and " below " can be
One feature is immediately below second feature or obliquely downward, or is merely representative of fisrt feature level height less than second feature.
In one aspect of the invention, the present invention proposes a kind of system processing house refuse.Reality according to the present invention
Executing example, with reference to Fig. 1, this system includes: pretreatment unit 100, heat accumulation type radiant tube revolving bed 200 and cement kiln are collaborative processes list
Unit 300.
According to embodiments of the invention, pretreatment unit 100 have house refuse entrance 101, foul smell outlet 102, organic
Garbage outlet 103, inorganic refuse outlet 104 and the first outlet of sewer 105, and be suitable to house refuse is carried out pretreatment, thus
Foul smell, organic waste, inorganic refuse and the first sewage can be obtained.Concrete, after house refuse is weighed by weighbridge office, through unloading
Material platform is poured refuse pit into and is carried out heap filter, obtains foul smell (being mainly composed of methane) and contaminant water, then will by garbage grab bucket
Rubbish after heap filter is sent in apron feeder, and uniform and stable for material is transported to belt with uniform distribution machine by apron feeder
On machine, rubbish is transported to manual sorting room by belt feeder, is sorted by the chaff interference such as inorganic refuse such as glass, brick and tile, branch, nettle
Out, then sieving through rotary screen, the organic waste obtained supplies after roll crushing crusher machine to subsequent process again and carries out
Process.
According to embodiments of the invention, heat accumulation type radiant tube revolving bed 200 has the first combustible gas entrance 201, combustion-supporting sky
Gas entrance 202, quick lime entrance 203, organic waste entrance 204, pyrolysis oil gas vent 205 and pyrolytic carbon outlet 206, combustion-supporting sky
Gas entrance 202 is connected with foul smell outlet 102, and organic waste entrance 204 is connected with organic waste outlet 103, and is suitable to foul smell
Supply to heat accumulation type radiant tube revolving bed uses as the combustion air of heat accumulation type radiant tube, and at heat accumulating type together with combustible gas
Radial canal burns for providing heat in revolving bed, quick lime and organic waste is supplied to revolving bed, carries out pyrolysis processing,
Such that it is able to obtain being pyrolyzed oil gas and pyrolytic carbon.Concrete, the organic waste from rubbish pretreatment unit is completely cutting off air
Under the conditions of in revolving bed pyrolysis oven, be heated to about 600~900 DEG C, its contained Organic substance and the volatile matter overwhelming majority analysis
Going out, obtain being pyrolyzed oil gas and two kinds of products of pyrolytic carbon after pyrolysis, the quick lime wherein added can be with in catalytic pyrolysis pyrolysis oil gas
Tar, thus improve the yield of pyrolysis gas.Ringwise, furnace bottom can connect the burner hearth of the heat accumulation type radiant tube revolving bed that pyrolysis uses
Continuous rotation, the organic waste obtained after pretreatment and quick lime, feeding device load in heat accumulation type radiant tube revolving bed,
Being laid in equably on furnace bottom, layer thickness about 40~800mm, furnace bottom machine drives furnace bottom to rotate continuously, is layered on furnace bottom
The bed of material rotates with furnace bottom, sequentially passes through the preheating section of stove, a conversion zone, two conversion zones and three conversion zones, is finally heated to
About 600~900 DEG C and complete pyrolytic reaction, the pyrolytic carbon after pyrolysis is unloaded by pyrolytic carbon outlet outside coming out of the stove, and immediately enters cold
But room cooling, pyrolysis oil gas is discharged from multiple pyrolysis oil gas vents of burner hearth.Inventor finds, by by house refuse pretreatment
After obtain organic waste, foul smell and cement raw material quick lime supply carry out at pyrolysis to heat accumulation type radiant tube revolving bed
Reason, quick lime can be with the pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas,
And this part quick lime can supply after pyrogenic processes to subsequent process and use as cement producting material, thus do not increasing
The wasting of resources that garbage loading embeading or burning cause can be avoided while adding processing cost, and can be effective by pyrolysis processing
The problem that brought two English that solve to burn away the refuse pollute.It should be noted that quick lime entrance 203 and organic waste entrance
204 can be single two entrances, it is also possible to for same entrance, those skilled in the art can be carried out according to actual needs
Select.
According to embodiments of the invention, cement kiln synergetic unit 300 have feed(raw material)inlet 301, fuel inlet 302,
Waste gas outlet 303 and cement exit 304, fuel inlet 302 is connected with pyrolytic carbon 206 outlet, feed(raw material)inlet 301 and inorganic refuse
Outlet 104 is connected, and is suitable to the pyrolytic carbon that obtained by heat accumulation type radiant tube revolving bed and inorganic refuse that pretreatment unit obtains
Supplying to cement kiln synergetic unit, pyrolytic carbon makes inorganic refuse and water as the fuel of cement kiln synergetic unit
Mud raw material carry out collaborative process, such that it is able to obtain waste gas and cement.Inventor finds, by by heat accumulation type radiant tube revolving bed
The inorganic refuse that the pyrolytic carbon obtained and pretreatment unit obtain supplies to cement kiln synergetic unit, and pyrolytic carbon is as water
The fuel of stall synergetic unit uses so that inorganic refuse and limestone, clay matter etc. occur as between cement slurry
Synergism, such that it is able to combine garbage disposal with cement kiln synergetic unit, relative to existing cement
Kiln cooperative disposal method, in this application, once cement kiln production line stops production, and house refuse can also be pyrolyzed in advance, Bu Huidui
Put smelly, produce the problem that rubbish can be put nowhere, and then realize the innoxious of house refuse and recycling treatment.Concrete, nothing
Machine rubbish is of low quality in the 15% of cement entirety raw material.
Concrete, with reference to Fig. 2, cement kiln synergetic unit 300 includes raw material grinding mill 31, homogenizing storehouse 32, preheater 33, divides
Solve stove 34, rotary kiln 35, clinker warehouse 36 and fine coal deployment device 37 etc., according to a particular embodiment of the invention, with reference to Fig. 2, heat
Solving charcoal outlet 206 to be connected with at least one in preheater 33, dore furnace 34, rotary kiln 35, cement slurry is through raw material grinding mill
31 carry out pulverizing and dried, supply successively to homogenizing storehouse 32, preheater 33, dore furnace 34, rotary kiln 35, clinker warehouse 36 and powder
Coal deployment device 37 processes, and obtains waste gas and cement products.Can increase online at raw material grinding mill for controlling material composition fluctuation
Analyser, such that it is able to save the input of cement raw material.
The system of process house refuse according to embodiments of the present invention is by organic by obtain after house refuse pretreatment
Rubbish, foul smell and the supply of cement raw material quick lime carry out pyrolysis processing to heat accumulation type radiant tube revolving bed, and quick lime is permissible
Pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this part is raw
Calx can supply after pyrogenic processes to subsequent process and use as cement producting material, thus is not increasing processing cost
The wasting of resources that garbage loading embeading or burning cause can be avoided simultaneously, and can effectively solve to burn away the refuse by pyrolysis processing
The problem that two English brought pollute, makes the supply of gained pyrolytic carbon as fuel to cement kiln synergetic unit simultaneously
With, pretreatment unit gained inorganic refuse supply to cement kiln synergetic unit will coordinate limestone, clay matter etc. to be used as
Cement slurry, is so possible not only to effectively reduce cement cost, and so that separating obtained inorganic refuse is able to abundant profit
With, such that it is able to garbage disposal is combined with cement kiln synergetic unit, work in coordination with relative to existing cement kiln
Method of disposal, in this application, once cement kiln production line stops production, and house refuse can also be pyrolyzed in advance, will not bank up smelly,
Produce the problem that rubbish can be put nowhere, thus realize the innoxious of house refuse and recycling treatment.
With reference to Fig. 3, according to embodiments of the invention, the system of described process house refuse farther includes: Oil-gas Separation
Purifier 400, combustible gas storage tank 500 and sewage-treatment plant 600.
According to embodiments of the invention, Oil-gas Separation purifier 400 has pyrolysis oil gas entrance 401, pyrolysis gas outlet
402, pyrolysis oil outlet 403 and the second outlet of sewer 404, pyrolysis oil gas entrance 401 is connected with pyrolysis oil gas vent 205, pyrolysis
Oil export 403 is connected with fuel inlet 302, and is suitable to the pyrolysis oil gas obtained in heat accumulation type radiant tube revolving bed for carrying out point
From purified treatment, such that it is able to isolated pyrolysis gas, pyrolysis oil and the second sewage, and obtained pyrolysis oil is supplied to water
Stall synergetic unit uses as fuel.Concrete, from the pyrolysis oil gas of heat accumulation type radiant tube revolving bed through wet type
Gas wash tower, after being removed by the dust carried, enters the transverse pipe initial cooler of two parallel operations, enters back into two also in pyrolysis oil gas
In conjunction with time operation electrical tar precipitator, complete to remove the tar work carried secretly in pyrolysis gas, then by coal gas Roots blower by heat
Vent one's spleen and deliver to dry desulfurization operation, gas-liquid separator separates the pyrolysis oil got off and circulation pyrolysis water enter mechanization profit and divide
From groove, it is circulated pyrolysis water, pyrolysis oil separating, i.e. isolated pyrolysis oil and sewage at this.It should be noted that ability
Actual conditions during this can be selected by field technique personnel according to actual needs.
According to embodiments of the invention, combustible gas storage tank 500 has the second combustible gas entrance 501 and the outlet of the second combustible gas
502, the second combustible gas entrance 501 is connected with pyrolysis gas outlet 402, the second combustible gas outlet 502 and the first combustible gas entrance 201
It is connected, and is suitable to store the combustible gas of Oil-gas Separation purifier isolated, and the supply of this combustible gas is radiated to heat accumulating type
Pipe revolving bed uses as the fuel of radial canal.Thus, it is possible to significantly reduce processing cost.
According to embodiments of the invention, sewage-treatment plant 600 has sewage inlet 601 and treatment fluid outlet 602, sewage
Entrance 601 is connected with the first outlet of sewer 105 and the second outlet of sewer 404 respectively, and is suitable to obtained by pretreatment unit
The second sewage that one sewage and Oil-gas Separation purifier obtain carries out purified treatment, such that it is able to obtain treatment fluid.Need
Bright, the actual conditions employed in this process can be selected by those skilled in the art according to actual needs.
According to a particular embodiment of the invention, with reference to Fig. 4, in pyrolysis oil outlet 402 and cement kiln synergetic unit
Preheater 33, dore furnace 34 are connected with the fuel inlet at least one in rotary kiln 35.Thus, it is possible to significantly reduce cement
Production cost.
With reference to Fig. 5, the system of process house refuse according to embodiments of the present invention farther includes: TRT 700.
According to embodiments of the invention, TRT 700 has exhaust gas entrance 701 and boiler residual air outlet 702, and waste gas enters
Mouth 701 is connected with waste gas outlet 303, and boiler residual air outlet 702 is connected with the raw material grinding mill 31 in cement kiln synergetic unit, and
The kiln tail gas supply being suitable to obtain quality coal in cement kiln systems processing unit carries out waste heat recovery to TRT, and by obtained
Boiler residual air use as dry medium to the raw material grinding mill on quality coal in cement kiln systems processing unit as thermal source supply.Thus, may be used
To significantly reduce system energy consumption.
As it has been described above, the system of process house refuse according to embodiments of the present invention can have selected from following advantage at least
One of:
The system of process house refuse according to embodiments of the present invention uses heat accumulation type radiant tube revolving bed to house refuse
It is pyrolyzed, it is to avoid burn the problem that two English brought pollute;
The system of process house refuse according to embodiments of the present invention is by being combined refuse pyrolysis with cement kiln production line
Getting up, take full advantage of the pyrolysis oil of refuse pyrolysis generation, pyrolysis gas, pyrolytic carbon, energy utilization rate is high;
The system of process house refuse according to embodiments of the present invention the most just adds quick lime, both to being pyrolyzed
To catalytic action, the link that later stage cement raw material adds can be saved again, change the technological process of conventional cement kiln;
Product after the refuse pyrolysis of the system of process house refuse according to embodiments of the present invention can be by cement kiln
Utilize, save the raw material required for cement kiln produces;
The system of process house refuse according to embodiments of the present invention combines with cement kiln skill relative to original rubbish
Art, this technology does not interferes with the production line of cement kiln itself, does not interferes with the quality of its product, and once cement kiln stops production,
House refuse can also process;
The system of process house refuse according to embodiments of the present invention improves the macroeconomic of refuse pyrolysis gasifying process
Property, it is easy to industrialization promotion.
In another aspect of the invention, the present invention proposes a kind of method processing house refuse.According to the present invention's
Embodiment, the method is that the system using above-mentioned process house refuse is carried out.According to a particular embodiment of the invention, with reference to figure
6, the method for described process house refuse includes:
S100: house refuse supply is carried out pretreatment to pretreatment unit
According to embodiments of the invention, house refuse supply is carried out pretreatment to pretreatment unit, such that it is able to
To foul smell, organic waste, inorganic refuse and the first sewage.Concrete, after house refuse is weighed by weighbridge office, through discharging platform
Pour refuse pit into and carry out heap filter, obtain foul smell (being mainly composed of methane) and contaminant water, after then being filtered by heap by garbage grab bucket
Rubbish send in apron feeder, uniform and stable for material is transported on belt feeder by apron feeder with uniform distribution machine,
Rubbish is transported to manual sorting room by belt feeder, is sorted out by the chaff interference such as inorganic refuse such as glass, brick and tile, branch, nettle,
Sieving through rotary screen, the organic waste obtained supplies after roll crushing crusher machine to subsequent process again and processes again.
S200: quick lime, organic waste and foul smell are supplied to heat accumulation type radiant tube revolving bed
According to embodiments of the invention, foul smell is supplied to heat accumulation type radiant tube revolving bed helping as heat accumulation type radiant tube
Combustion air uses, and burns in heat accumulation type radiant tube together with combustible gas for providing heat in revolving bed, by quick lime and having
The supply of machine rubbish carries out pyrolysis processing to revolving bed, such that it is able to obtain being pyrolyzed oil gas and pyrolytic carbon.Concrete, from rubbish
The organic waste of pretreatment unit is heated to about 600~900 DEG C under conditions of isolation air in revolving bed pyrolysis oven, its
Contained Organic substance and the volatile matter overwhelming majority separate out, and obtain being pyrolyzed oil gas and two kinds of products of pyrolytic carbon, wherein add after pyrolysis
Quick lime thus the yield of pyrolysis gas can be improved with the tar in catalytic pyrolysis pyrolysis oil gas.The heat accumulating type spoke that pyrolysis uses
Penetrating the burner hearth of pipe revolving bed ringwise, furnace bottom can rotate continuously, the organic waste obtained after pretreatment and quick lime, by filling
Material device loads in heat accumulation type radiant tube revolving bed, is laid in equably on furnace bottom, layer thickness about 40~800mm, furnace bottom machine
Tool drive furnace bottom rotate continuously, the bed of material being layered on furnace bottom with furnace bottom rotate, sequentially pass through the preheating section of stove, a conversion zone,
Two conversion zones and three conversion zones, be finally heated to about 600~900 DEG C and complete pyrolytic reaction, the pyrolytic carbon after pyrolysis by
Pyrolytic carbon outlet is unloaded outside coming out of the stove, and immediately enters cooling chamber cooling, and pyrolysis oil gas is discharged from multiple pyrolysis oil gas vents of burner hearth.
Inventor finds, is supplied extremely by the organic waste that will obtain after house refuse pretreatment, foul smell and cement raw material quick lime
Carrying out pyrolysis processing in heat accumulation type radiant tube revolving bed, quick lime can be pyrolyzed the pyrolysis oil in oil gas with catalytic pyrolysis gained, from
And can significantly improve the yield of gained pyrolysis gas, and this part quick lime can supply to subsequent process after pyrogenic processes
Use as cement producting material, thus the money that garbage loading embeading or burning cause can be avoided while not increasing processing cost
Source is wasted, and can effectively be solved to burn away the refuse the problem that two brought English pollute by pyrolysis processing.
S300: inorganic refuse and pyrolytic carbon supply are made inorganic refuse and cement slurry to cement kiln synergetic unit
Carry out collaborative process
According to embodiments of the invention, the pyrolytic carbon obtained by heat accumulation type radiant tube revolving bed and pretreatment unit obtain
Inorganic refuse supplies to cement kiln synergetic unit, and pyrolytic carbon makes inorganic as the fuel of cement kiln synergetic unit
Rubbish and cement slurry carry out collaborative process, such that it is able to obtain waste gas and cement.Inventor finds, by being radiated by heat accumulating type
Pyrolytic carbon that pipe revolving bed obtains and the inorganic refuse that pretreatment unit obtains supply in cement kiln synergetic unit, pyrolysis
Charcoal uses as the fuel of cement kiln synergetic unit so that inorganic refuse and limestone, clay matter etc. are as cement slurry
Between occur synergism, such that it is able to garbage disposal is combined with cement kiln synergetic unit, relative to show
Some cement kiln synergic processing methods, in this application, once cement kiln production line stops production, and house refuse can also be hot in advance
Solve, will not bank up smelly, produce the problem that rubbish can be put nowhere, and then realize the innoxious of house refuse and recycling treatment.
Concrete, inorganic refuse is of low quality in the 15% of cement entirety raw material.
According to a particular embodiment of the invention, the pyrolytic carbon that can be obtained by heat accumulation type radiant tube revolving bed supplies extremely and water
At least one in preheater, dore furnace and rotary kiln in stall synergetic unit uses as fuel.Thus, it is possible to it is aobvious
Write and reduce manufacture of cement cost.
The method of process house refuse according to embodiments of the present invention is by organic by obtain after house refuse pretreatment
Rubbish, foul smell and the supply of cement raw material quick lime carry out pyrolysis processing to heat accumulation type radiant tube revolving bed, and quick lime is permissible
Pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this part is raw
Calx can supply after pyrogenic processes to subsequent process and use as cement producting material, thus is not increasing processing cost
The wasting of resources that garbage loading embeading or burning cause can be avoided simultaneously, and can effectively solve to burn away the refuse by pyrolysis processing
The problem that two English brought pollute, makes the supply of gained pyrolytic carbon as fuel to cement kiln synergetic unit simultaneously
With, pretreatment unit gained inorganic refuse supply to cement kiln synergetic unit will coordinate limestone, clay matter etc. to be used as
Cement slurry, is so possible not only to effectively reduce cement cost, and so that separating obtained inorganic refuse is able to abundant profit
With, such that it is able to garbage disposal is combined with cement kiln synergetic unit, work in coordination with relative to existing cement kiln
Method of disposal, in this application, once cement kiln production line stops production, and house refuse can also be pyrolyzed in advance, will not bank up smelly,
Produce the problem that rubbish can be put nowhere, thus realize the innoxious of house refuse and recycling treatment.
With reference to Fig. 7, according to embodiments of the invention, the method for described process house refuse farther includes:
S400: the supply of pyrolysis oil gas is carried out isolation of purified process to Oil-gas Separation purifier, and by gained pyrolysis gas
Supply and use as combustion gas to heat accumulation type radiant tube revolving bed, obtained pyrolysis oil is supplied to cement kiln synergetic unit
Use as fuel
According to embodiments of the invention, by the pyrolysis oil gas obtained in heat accumulation type radiant tube revolving bed for carrying out isolation of purified
Process, such that it is able to isolated pyrolysis gas, pyrolysis oil and the second sewage, and obtained pyrolysis oil supply is assisted to cement kiln
Use as fuel with processing unit.Concrete, from the pyrolysis oil gas of heat accumulation type radiant tube revolving bed through wet dedusting tower,
After being removed by the dust carried in pyrolysis oil gas, enter the transverse pipe initial cooler of two parallel operations, enter back into two parallel connections simultaneously
The electrical tar precipitator of operation, completes to remove the tar work carried secretly in pyrolysis gas, then will be pyrolyzed pneumatic transmission by coal gas Roots blower
Mechanization oil-water separation tank is entered to dry desulfurization operation, the gas-liquid separator separates pyrolysis oil got off and circulation pyrolysis water,
Pyrolysis water, pyrolysis oil separating, i.e. isolated pyrolysis oil and sewage it is circulated at this.It should be noted that this area skill
Actual conditions during this can be selected by art personnel according to actual needs.
According to a particular embodiment of the invention, the pyrolysis oil of Oil-gas Separation purifier isolated can be supplied to
At least one in preheater, dore furnace and rotary kiln in cement kiln synergetic unit uses as fuel.Thus, it is possible to
Significantly reduce manufacture of cement cost.
The second sewage that S500: the first sewage obtained by S100 and S400 obtain supplies to sewage-treatment plant
According to embodiments of the invention, the first sewage obtained by pretreatment unit and Oil-gas Separation purifier obtain
Second sewage carries out purified treatment, such that it is able to obtain treatment fluid.It should be noted that those skilled in the art can be according to reality
Border needs to select the actual conditions employed in this process.
With reference to Fig. 8, according to embodiments of the invention, the method for described process house refuse farther includes:
S600: waste gas supply to the TRT obtained by S300 carries out UTILIZATION OF VESIDUAL HEAT IN, and supplies boiler residual air to water
Raw material grinding mill in stall synergetic unit
According to embodiments of the invention, waste gas step S300 obtained supply carries out UTILIZATION OF VESIDUAL HEAT IN to TRT, from
And boiler residual air can be obtained, and using the raw material grinding mill in boiler residual air supply to cement kiln synergetic unit as dry medium
Use.Thus, it is possible to significantly reduce energy consumption.
Below with reference to specific embodiment, present invention is described, it should be noted that these embodiments are only to describe
Property, and limit the present invention never in any form.
Embodiment
Certain city's house refuse is processed by the system using the process house refuse shown in Fig. 9, and house refuse becomes packet
Become as shown in table 1:
Table 1 house refuse becomes to be grouped into (wt%)
A, pretreatment unit carry out pretreatment: after house refuse is weighed by weighbridge office, pour rubbish into through discharging platform
Storage hole carries out heap filter, obtains foul smell (being mainly composed of methane) and contaminant water, and the rubbish after then being filtered by heap by garbage grab bucket send
Entering in apron feeder, uniform and stable for material is transported on belt feeder by apron feeder with uniform distribution machine, and belt feeder will
Rubbish is transported to manual sorting room, is sorted out by the chaff interference such as inorganic refuse such as glass, brick and tile, branch, nettle, then through cylinder
Sieving, the organic waste obtained supplies to heat accumulation type radiant tube revolving bed after roll crushing crusher machine again;
B, heat accumulation type radiant tube revolving bed are pyrolyzed: by quick lime and from the foul smell of rubbish pretreatment unit and organic rubbish
Rubbish supply is heated to 800 DEG C of left sides to heat accumulation type radiant tube revolving bed under conditions of isolation air in revolving bed pyrolysis oven
The right side, its contained Organic substance and the volatile matter overwhelming majority separate out, and obtain being pyrolyzed oil gas and two kinds of products of pyrolytic carbon after pyrolysis.Pyrolysis
Ringwise, furnace bottom can rotate the burner hearth of the heat accumulation type radiant tube revolving bed used continuously, the organic rubbish obtained after pretreatment
Rubbish, is loaded in heat accumulation type radiant tube revolving bed by feeding device, is laid in equably on furnace bottom, layer thickness about 700mm, furnace bottom
Machinery drives furnace bottom to rotate continuously, and the bed of material being layered on furnace bottom rotates with furnace bottom, sequentially passes through the preheating section of stove, a reaction
Section, two conversion zones and three conversion zones, be finally heated to about 800 DEG C and complete pyrolytic reaction, and the pyrolytic carbon after pyrolysis is by warm
Solution charcoal outlet is unloaded outside coming out of the stove, and immediately enters cooling chamber cooling, and pyrolysis oil gas is discharged from multiple pyrolysis oil gas vents of burner hearth.
C, cement kiln synergetic unit carry out collaborative process: the pyrolytic carbon obtained by heat accumulation type radiant tube revolving bed supplies
Preheater, dore furnace and rotary kiln to cement kiln synergetic unit use as fuel, fill from house refuse pretreatment
Inorganic matter warehouse in the cement plant that the inorganic refuse put send, delivers on the feed belt of raw material grinding mill after grab bucket feeding, metering,
After dispensing, enter raw material grinding mill with raw material carry out pulverizing and be dried, can increase in raw material grinding mill system for controlling material composition fluctuation
Line analysis instrument.Inorganic refuse on the one hand alternative part clay raw material, saves cement raw material and puts into, on the other hand inorganic refuse
In poisonous and harmful substance achieve harmless treatment through cement solidification effect, and inorganic refuse gross mass is not higher than cement
The 5% of overall proportion scale, kiln tail gas supply cement kiln synergetic unit obtained carries out waste heat to TRT and returns
Receive, and the raw material grinding mill that obtained boiler residual air supply is worked in coordination with in processing means to cement kiln is used as dry medium.
D, Oil-gas Separation purifier carry out being pyrolyzed oil gas purification separation: from the pyrolysis oil of heat accumulation type radiant tube revolving bed
Gas is through wet dedusting tower, after being removed by the dust carried, enters the transverse pipe initial cooler of two parallel operations in pyrolysis oil gas, then
Enter the electrical tar precipitator that two parallel connections operate simultaneously, complete to remove the tar work carried secretly in pyrolysis gas, then by coal gas Roots
Pyrolysis gas is delivered to dry desulfurization operation, the gas-liquid separator separates pyrolysis oil got off and circulation pyrolysis water and is entered machine by aerator
Tool oil-water separation tank, is circulated pyrolysis water, pyrolysis oil separating, i.e. isolated pyrolysis oil and sewage, and will divide at this
It is stored in combustible gas storage tank from the pyrolysis gas obtained, and supplies to heat accumulation type radiant tube revolving bed as spoke through combustible gas storage tank
Penetrate pipe combustion gas to use, the preheater of pyrolysis oil that Oil-gas Separation purifier is obtained supply to cement kiln synergetic unit,
Dore furnace and rotary kiln use as fuel, are supplied by gained sewage in Oil-gas Separation purifier gained sewage and pretreatment unit
Process to sewage-treatment plant.
Composition and the calorific value of pyrolytic carbon are as shown in table 2:
Table 2 pyrolytic carbon composition and calorific value
In the description of this specification, reference term " embodiment ", " some embodiments ", " example ", " specifically show
Example " or the description of " some examples " etc. means to combine this embodiment or example describes specific features, structure, material or spy
Point is contained at least one embodiment or the example of the present invention.In this manual, to the schematic representation of above-mentioned term not
Identical embodiment or example must be directed to.And, the specific features of description, structure, material or feature can be in office
One or more embodiments or example combine in an appropriate manner.Additionally, in the case of the most conflicting, the skill of this area
The feature of the different embodiments described in this specification or example and different embodiment or example can be tied by art personnel
Close and combination.
Although above it has been shown and described that embodiments of the invention, it is to be understood that above-described embodiment is example
Property, it is impossible to being interpreted as limitation of the present invention, those of ordinary skill in the art within the scope of the invention can be to above-mentioned
Embodiment is changed, revises, replaces and modification.
Claims (10)
1. the system processing house refuse, it is characterised in that including:
Pretreatment unit, described pretreatment unit has house refuse entrance, foul smell outlet, organic waste outlet, inorganic refuse
Outlet and the first outlet of sewer;
Heat accumulation type radiant tube revolving bed, described heat accumulation type radiant tube revolving bed have the first combustible gas entrance, combustion air inlet,
Quick lime entrance, organic waste entrance, pyrolysis oil gas vent and pyrolytic carbon outlet, described combustion air inlet goes out with described foul smell
Mouth is connected, and described organic waste entrance is connected with the outlet of described organic waste;
Cement kiln synergetic unit, described cement kiln synergetic unit have feed(raw material)inlet, fuel inlet, waste gas outlet and
Cement exit, described feed(raw material)inlet is connected with the outlet of described inorganic refuse, and described fuel inlet is connected with the outlet of described pyrolytic carbon.
System the most according to claim 1, it is characterised in that farther include:
Oil-gas Separation purifier, described Oil-gas Separation purifier has pyrolysis oil gas entrance, pyrolysis gas outlet, pyrolysis oil go out
Mouth and the second outlet of sewer, described pyrolysis oil gas entrance is connected with described pyrolysis oil gas vent, and described pyrolysis oil exports with described
Fuel inlet is connected;
Combustible gas storage tank, described combustible gas storage tank has the second combustible gas entrance and the outlet of the second combustible gas, described second flammable
Gas entrance is connected with described pyrolysis gas outlet, and described second combustible gas outlet is connected with described first combustible gas entrance;
Sewage-treatment plant, described sewage-treatment plant have sewage inlet and treatment fluid outlet, described sewage inlet respectively with
Described first outlet of sewer is connected with described second outlet of sewer.
System the most according to claim 1 and 2, it is characterised in that described pyrolytic carbon outlet place collaborative with described cement kiln
Preheater, dore furnace on reason unit are connected with the fuel inlet at least one in rotary kiln.
4. according to the system according to any one of claim 1-3, it is characterised in that the outlet of described pyrolysis oil and described cement kiln
Preheater, dore furnace in synergetic unit are connected with the fuel inlet at least one in rotary kiln.
5. according to the system according to any one of claim 1-4, it is characterised in that farther include:
TRT, described TRT has exhaust gas entrance and the outlet of boiler residual air, and described exhaust gas entrance goes out with described waste gas
Mouth is connected, and the outlet of described boiler residual air is connected with the raw material grinding mill in described cement kiln synergetic unit.
6. use the method that the system of the process house refuse according to any one of Claims 1 to 5 processes house refuse,
It is characterized in that, including:
(1) will house refuse supply to described pretreatment unit carries out pretreatment, in order to obtain foul smell, organic waste, inorganic
Rubbish and the first sewage;
(2) by the supply of quick lime, described organic waste and described foul smell to described heat accumulation type radiant tube revolving bed, in order to described
Organic waste carries out pyrolysis processing, obtains being pyrolyzed oil gas and pyrolytic carbon;
(3) described inorganic refuse and described pyrolytic carbon are supplied extremely described cement kiln synergetic unit and make described inorganic refuse
Collaborative process is carried out, in order to obtain waste gas and cement with cement slurry.
Method the most according to claim 6, it is characterised in that farther include:
(4) supply of described pyrolysis oil gas is carried out isolation of purified process to described Oil-gas Separation purifier, in order to be pyrolyzed
Air and heat solution oil and the second sewage, and the supply of described pyrolysis gas is used to described heat accumulation type radiant tube revolving bed as combustion gas, will
The supply of described pyrolysis oil uses to described cement kiln synergetic unit as fuel;
(5) the described second sewage supply that described first sewage step (1) obtained and step (4) obtain fills to sewage disposal
Put, in order to obtain treatment fluid.
8. according to the method described in claim 6 or 7, it is characterised in that described pyrolytic carbon step (2) obtained supplies to institute
At least one stated in the preheater in cement kiln synergetic unit, dore furnace and rotary kiln uses as fuel.
9. according to the method according to any one of claim 6-8, it is characterised in that the described pyrolysis oil that step (4) is obtained
At least one in preheater, dore furnace and rotary kiln in supply extremely described cement kiln synergetic unit makes as fuel
With.
10. according to the method according to any one of claim 6-9, it is characterised in that farther include:
(6) described waste gas supply step (3) obtained carries out UTILIZATION OF VESIDUAL HEAT IN to described TRT, in order to obtain boiler residual
Gas, and the supply of described boiler residual air is used to the raw material grinding mill in described cement kiln synergetic unit as dry medium.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610430277.7A CN106077024A (en) | 2016-06-16 | 2016-06-16 | Process the system and method for house refuse |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610430277.7A CN106077024A (en) | 2016-06-16 | 2016-06-16 | Process the system and method for house refuse |
Publications (1)
Publication Number | Publication Date |
---|---|
CN106077024A true CN106077024A (en) | 2016-11-09 |
Family
ID=57235578
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201610430277.7A Pending CN106077024A (en) | 2016-06-16 | 2016-06-16 | Process the system and method for house refuse |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106077024A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105903752A (en) * | 2016-06-16 | 2016-08-31 | 北京神雾环境能源科技集团股份有限公司 | Household garbage treatment system and method |
CN110586609A (en) * | 2019-08-12 | 2019-12-20 | 中原环资科技有限公司 | Hazardous waste treatment process with pyrolysis and ceramsite sintering synergistic |
Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2720479A1 (en) * | 1994-05-30 | 1995-12-01 | Inst Francais Du Petrole | Process and installation of pyrolysis of waste having a preheating unit |
JP2000310408A (en) * | 1999-04-26 | 2000-11-07 | Rasa Shoji Kk | Method and facility for refuse disposal |
CN1430016A (en) * | 2002-12-24 | 2003-07-16 | 鞍山热能研究院 | Slag incinerator for treating hazardous wastes and medical garbage and process method |
CN102504843A (en) * | 2011-11-21 | 2012-06-20 | 北京神雾环境能源科技集团股份有限公司 | Heat accumulation type fuel gas radiation pipe rotary hearth furnace domestic garbage dry distillation method |
CN102706140A (en) * | 2012-05-29 | 2012-10-03 | 倪文龙 | Pyrolysis garbage technology performed by means of double-cylinder rotary kiln |
CN203791331U (en) * | 2014-03-24 | 2014-08-27 | 北京凯盛建材工程有限公司 | System for synergistic treatment of municipal domestic waste in cement kiln |
CN203923026U (en) * | 2014-07-02 | 2014-11-05 | 南京凯盛国际工程有限公司 | A kind of system of cement kiln synergic processing domestic refuse |
CN204544958U (en) * | 2015-04-03 | 2015-08-12 | 坚构(北京)建筑技术有限公司 | Cement rotary kiln associated treatment house refuse and energy comprehensive utilization system |
CN104907311A (en) * | 2015-05-15 | 2015-09-16 | 石家庄新华能源环保科技股份有限公司 | Method and device for garbage processing water recovery and pure carbon production |
CN105542808A (en) * | 2016-02-22 | 2016-05-04 | 王志成 | All-closed zero-emission household refuse energy regeneration and comprehensive utilization production process |
CN206519427U (en) * | 2016-06-16 | 2017-09-26 | 神雾科技集团股份有限公司 | The system for handling house refuse |
-
2016
- 2016-06-16 CN CN201610430277.7A patent/CN106077024A/en active Pending
Patent Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2720479A1 (en) * | 1994-05-30 | 1995-12-01 | Inst Francais Du Petrole | Process and installation of pyrolysis of waste having a preheating unit |
JP2000310408A (en) * | 1999-04-26 | 2000-11-07 | Rasa Shoji Kk | Method and facility for refuse disposal |
CN1430016A (en) * | 2002-12-24 | 2003-07-16 | 鞍山热能研究院 | Slag incinerator for treating hazardous wastes and medical garbage and process method |
CN102504843A (en) * | 2011-11-21 | 2012-06-20 | 北京神雾环境能源科技集团股份有限公司 | Heat accumulation type fuel gas radiation pipe rotary hearth furnace domestic garbage dry distillation method |
CN102706140A (en) * | 2012-05-29 | 2012-10-03 | 倪文龙 | Pyrolysis garbage technology performed by means of double-cylinder rotary kiln |
CN203791331U (en) * | 2014-03-24 | 2014-08-27 | 北京凯盛建材工程有限公司 | System for synergistic treatment of municipal domestic waste in cement kiln |
CN203923026U (en) * | 2014-07-02 | 2014-11-05 | 南京凯盛国际工程有限公司 | A kind of system of cement kiln synergic processing domestic refuse |
CN204544958U (en) * | 2015-04-03 | 2015-08-12 | 坚构(北京)建筑技术有限公司 | Cement rotary kiln associated treatment house refuse and energy comprehensive utilization system |
CN104907311A (en) * | 2015-05-15 | 2015-09-16 | 石家庄新华能源环保科技股份有限公司 | Method and device for garbage processing water recovery and pure carbon production |
CN105542808A (en) * | 2016-02-22 | 2016-05-04 | 王志成 | All-closed zero-emission household refuse energy regeneration and comprehensive utilization production process |
CN206519427U (en) * | 2016-06-16 | 2017-09-26 | 神雾科技集团股份有限公司 | The system for handling house refuse |
Non-Patent Citations (1)
Title |
---|
王建芳: "《水泥工业余热发电及其工程》", 31 October 2011, 中国建材工业出版社 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105903752A (en) * | 2016-06-16 | 2016-08-31 | 北京神雾环境能源科技集团股份有限公司 | Household garbage treatment system and method |
CN110586609A (en) * | 2019-08-12 | 2019-12-20 | 中原环资科技有限公司 | Hazardous waste treatment process with pyrolysis and ceramsite sintering synergistic |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105032884B (en) | Cement rotary kiln collaboration processes house refuse and energy comprehensive utilization system and method | |
CN105972604B (en) | A kind of house refuse pretreatment system and method for being coupled in cement kiln synergic processing | |
CN107339702A (en) | A kind of method of cement kiln synergic processing urban and rural domestic refuse | |
CN205402733U (en) | Domestic waste and/or industrial waste's processing production line | |
CN102357516A (en) | Linkage process of municipal waste pre-treatment and cement kiln resource comprehensive utilization and system thereof | |
CN105855274A (en) | Household garbage disposal system and method | |
CN109824271A (en) | It handles the method for house refuse and implements its system | |
CN112066384A (en) | Straw household garbage waste bundling and pyrolysis cooperative treatment method | |
CN106077023A (en) | Process the system and method for house refuse | |
CN205667982U (en) | The processing system of one way of life rubbish | |
CN206661886U (en) | The system for handling house refuse | |
CN106077024A (en) | Process the system and method for house refuse | |
CN206316118U (en) | The system for handling house refuse | |
CN206519427U (en) | The system for handling house refuse | |
CN205635475U (en) | Organic garbage pyrolytic system | |
CN105694925B (en) | Organic waste pyrolysis system and its application | |
CN107631304A (en) | A kind of smoke circulating system suitable for cement kiln synergic processing house refuse | |
CN105754622A (en) | Organic garbage pyrolysis system and application thereof | |
CN110201980A (en) | The system and method for handling house refuse | |
CN105885884A (en) | Organic waste pyrolysis system and application thereof | |
CN206316117U (en) | The system for handling house refuse | |
CN206316116U (en) | The system for handling house refuse | |
CN106077025A (en) | Process the system and method for house refuse | |
CN205635474U (en) | Organic garbage pyrolytic system | |
CN205782961U (en) | A kind of house refuse pretreatment system being coupled in cement kiln synergic processing |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
CB02 | Change of applicant information | ||
CB02 | Change of applicant information |
Address after: 102200 Beijing city Changping District Machi Town cow Road No. 18 Applicant after: Shenwu science and technology group Limited by Share Ltd Address before: 102200 Beijing city Changping District Machi Town cow Road No. 18 Applicant before: Beijing Shenwu Environment Energy Technology Group Co., Ltd. |