CN105903752A - Household garbage treatment system and method - Google Patents

Household garbage treatment system and method Download PDF

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Publication number
CN105903752A
CN105903752A CN201610431684.XA CN201610431684A CN105903752A CN 105903752 A CN105903752 A CN 105903752A CN 201610431684 A CN201610431684 A CN 201610431684A CN 105903752 A CN105903752 A CN 105903752A
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CN
China
Prior art keywords
outlet
gas
pyrolysis
cement
inlet
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CN201610431684.XA
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Chinese (zh)
Inventor
贾懿曼
包欣欣
肖磊
王鹏飞
吴道洪
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Beijing Shenwu Environmental and Energy Technology Co Ltd
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Beijing Shenwu Environmental and Energy Technology Co Ltd
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Priority to CN201610431684.XA priority Critical patent/CN105903752A/en
Publication of CN105903752A publication Critical patent/CN105903752A/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass

Abstract

The invention discloses a household garbage treatment system and method. The system comprises a pretreatment device, a heat storing type radiant tube rotating bed and a cement kiln co-treating unit, wherein the pretreatment device is provided with a household garbage inlet, a smell outlet, an organic garbage outlet, an inorganic garbage outlet and a first sewage outlet; the heat storing type radiant tube rotating bed is provided with a first combustible gas inlet, a combustion-supporting air inlet, a quicklime inlet, an organic garbage inlet, a pyrolytic oil gas outlet and a pyrolytic carbon outlet; the combustion-supporting air inlet is connected with the smell outlet; the organic garbage inlet is connected with the organic garbage outlet; the cement kiln co-treating unit is provided with a raw material inlet, a fuel inlet, a waste gas outlet and a cement outlet; the fuel inlet is connected with the pyrolytic carbon outlet. With the adoption of the system, the production cost of cement can be effectively reduced; in addition, the harmless and resourceful treatment of the household garbage can be achieved, so that the system is high in economic benefit and social benefit.

Description

Process the system and method for house refuse
Technical field
The invention belongs to chemical technology field, specifically, the present invention relates to a kind of system and method processing house refuse.
Background technology
At present, the process problem of domestic waste becomes whole people's focus of attention already.Existing landfill, compost, burning etc. Technology is due to himself intrinsic shortcoming so that it is development is limited to.China many urban construction domestic garbage burning electricity generation Factory, but burn the two English pollution problems brought and cause people's dispute to waste incineration mode.Two English environmental toxicities are big, The most degradable, cause great threat to resident is healthy.The method using cement kiln synergic processing rubbish, existing technology Have after rubbish is directly burned or directly garbage raw material thrown away in cement kiln.Directly burn away the refuse dirts such as can producing two English Dye environment, produces 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 one of the present invention Purpose is to propose a kind of system and method processing house refuse, and this system is by assisting the process of house refuse with cement kiln Combine with treatment technology, be possible not only to effectively reduce manufacture of cement cost, and the nothing of house refuse can be realized Evilization and recycling treatment, have huge economic benefit and social benefit.
In the first aspect of the invention, this present invention proposes a kind of system processing house refuse.Reality according to the present invention Executing example, this system includes:
Pretreatment unit, described pretreatment unit has house refuse entrance, foul smell outlet, organic waste outlet, inorganic rubbish Rubbish 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 and 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 outlet And cement exit, described fuel inlet is connected with the outlet of described pyrolytic carbon.
Thus, 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, 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 and send out 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 a following additional technical characteristic:
In some embodiments of the invention, the system of described process house refuse farther includes: Oil-gas Separation purifier, Described Oil-gas Separation purifier has pyrolysis oil gas entrance, pyrolysis gas outlet, pyrolysis oil outlet and the second outlet of sewer, institute State pyrolysis oil gas entrance to be connected with described pyrolysis oil gas vent;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 combustible gas entrance is connected with described pyrolysis gas outlet, and described second combustible gas goes out Mouth is connected with described first combustible gas entrance;Sewage-treatment plant, described sewage-treatment plant has sewage inlet and treatment fluid Outlet, described sewage inlet is connected with described first outlet of sewer and described second outlet of sewer respectively.Thus, it is possible to it is notable Improve the environmental benefit of this system.
In some embodiments of the invention, the outlet of described inorganic refuse is connected with described feed(raw material)inlet.Thus, it is possible to it is notable Reduce manufacture of cement cost.
In some embodiments of the invention, described pyrolytic carbon outlet with described cement kiln synergetic unit on preheater, Dore furnace is connected with the fuel inlet at least one in rotary kiln.Thus, it is possible to reduce manufacture of cement cost further.
In some embodiments of the invention, the system of described process house refuse farther includes: TRT, described Electric installation 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 air 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.Enforcement according to the present invention Example, the method is that the system using process house refuse described above is carried out.According to a particular embodiment of the invention, should Method includes:
(1) house refuse supply is carried out pretreatment to described pretreatment unit, in order to obtain foul smell, organic waste, nothing Machine 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 institute State organic waste and carry out pyrolysis processing, obtain being pyrolyzed oil gas and pyrolytic carbon;
(3) cement slurry is made to carry out collaborative place as fuel described pyrolytic carbon supply to described cement kiln synergetic unit Reason, in order to obtain waste gas and cement.
Thus, the method for 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, 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 and send out 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 a following additional technical characteristic:
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 the second sewage, And the supply of described pyrolysis gas is used to described heat accumulation type radiant tube revolving bed as combustion gas;(5) institute that step (1) is obtained State the first sewage and described second sewage that step (4) obtains supplies to sewage-treatment plant, in order to obtain treatment fluid.Thus, The environmental benefit of this system can be significantly improved.
In some embodiments of the invention, the method for described process house refuse farther includes: step (1) is obtained by (6) To the supply of described inorganic refuse to described cement kiln synergetic unit carries out described collaborative process.Thus, it is possible to it is notable Reduce manufacture of cement cost.
In some embodiments of the invention, the method for described process house refuse farther includes: step (2) obtained At least one in preheater, dore furnace and rotary kiln in described pyrolytic carbon supply extremely described cement kiln synergetic unit is made Use for fuel.Thus, it is possible to reduce manufacture of cement cost further.
In some embodiments of the invention, the method for described process house refuse farther includes: step (3) is obtained by (7) To the supply of described waste gas carry out UTILIZATION OF VESIDUAL HEAT IN to described TRT, in order to obtain boiler residual air, and by described boiler residual air Supply uses to the raw material grinding mill in described cement kiln synergetic unit as dry medium.Thus, it is possible to significantly reduce system Energy consumption.
The additional aspect of the present invention and advantage will part be given in the following description, and part will become bright from the following description Aobvious, 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 will be apparent from from combining the accompanying drawings below description to embodiment 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 method flow schematic diagram of the process house refuse according to another embodiment of the present invention;
Figure 10 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 identical Or similar label represents same or similar element or has the element of same or like function.Retouch below with reference to accompanying drawing The embodiment stated 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 ", Orientation or the position relationship of the instruction such as " clockwise ", " counterclockwise ", " axially ", " radially ", " circumferential " are based on shown in the drawings Orientation or position relationship, be for only for ease of describe the present invention and simplify describe rather than instruction or hint indication device or Element 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 Person implies the 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 etc., unless otherwise expressly limited specifically.
In the present invention, unless otherwise clearly defined and limited, term " install ", " being connected ", " connection ", the art such as " fixing " Language 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 machinery 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, can be two units Connection within part or the interaction relationship of two elements, unless otherwise clear and definite restriction.Ordinary skill for this area For personnel, 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 can be One directly contacts with second feature, or the first and second features are by intermediary mediate contact.And, fisrt feature is Two features " on ", " top " and " above " but fisrt feature directly over second feature or oblique upper, or be merely representative of first Characteristic level height is higher than second feature.Fisrt feature second feature " under ", " lower section " and " below " can be fisrt feature Immediately below second feature or obliquely downward, or it 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.According to embodiments of the invention, With reference to Fig. 1, this system includes: pretreatment unit 100, heat accumulation type radiant tube revolving bed 200 and cement kiln synergetic unit 300。
According to embodiments of the invention, pretreatment unit 100 has house refuse entrance 101, foul smell outlet 102, organic rubbish Rubbish 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, Pour refuse pit into through discharging platform and carry out heap filter, obtain foul smell (being mainly composed of methane) and contaminant water, then by rubbish The rubbish after being filtered by heap of grabbing bucket is sent in apron feeder, and apron feeder and uniform distribution machine are by conveying uniform and stable for material On belt feeder, rubbish is transported to manual sorting room by belt feeder, by nothings such as chaff interference such as glass, brick and tile, branch, nettles Machine garbage sorting out, then sieves through rotary screen, the organic waste obtained supply after roll crushing crusher machine again to after Continuous process processes.
According to embodiments of the invention, heat accumulation type radiant tube revolving bed 200 has the first combustible gas entrance 201, combustion air Entrance 202, quick lime entrance 203, organic waste entrance 204, pyrolysis oil gas vent 205 and pyrolytic carbon outlet 206, help Combustion air intake 202 is connected with foul smell outlet 102, and organic waste entrance 204 is connected with organic waste outlet 103, and suitable In the foul smell supply combustion air to heat accumulation type radiant tube revolving bed as heat accumulation type radiant tube is used, and with the first combustible gas Burn in heat accumulation type radiant tube together for providing heat in revolving bed, supply to enter to revolving bed by quick lime and organic waste Row pyrolysis processing, such that it is able to obtain being pyrolyzed oil gas and pyrolytic carbon.Concrete, from the organic waste of rubbish pretreatment unit In revolving bed pyrolysis oven, about 600~900 DEG C it are heated to, its contained Organic substance and volatile matter under conditions of isolation air The overwhelming majority separates out, and obtains being pyrolyzed oil gas and two kinds of products of pyrolytic carbon after pyrolysis, and the quick lime wherein added can be with catalytic pyrolysis Tar in pyrolysis oil gas, thus improve the yield of pyrolysis gas.The burner hearth of the heat accumulation type radiant tube revolving bed that pyrolysis uses is ring Shape, furnace bottom can rotate continuously, the organic waste obtained after pretreatment and quick lime, feeding device load heat accumulating type spoke Penetrating in pipe revolving bed, be laid in equably on furnace bottom, layer thickness about 40~800mm, furnace bottom machine drives furnace bottom to turn continuously Dynamic, the bed of material being layered on furnace bottom rotates with furnace bottom, sequentially passes through the preheating section of stove, a conversion zone, two conversion zones and three anti- The section of answering, is finally heated to about 600~900 DEG C and completes pyrolytic reaction, and the pyrolytic carbon after pyrolysis is drawn off by pyrolytic carbon outlet Outside stove, and immediately entering cooling chamber cooling, pyrolysis oil gas is discharged from multiple pyrolysis oil gas vents of burner hearth.Inventor finds, Supplied to heat accumulation type radiant tube by the organic waste that will obtain after house refuse pretreatment, foul smell and cement raw material quick lime Carrying out pyrolysis processing in revolving bed, quick lime can be with the pyrolysis oil in catalytic pyrolysis gained pyrolysis oil gas, such that it is able to significantly carry The yield of high gained pyrolysis gas, and this part quick lime can supply to subsequent process as manufacture of cement after pyrogenic processes Raw material uses, thus can avoid the wasting of resources that garbage loading embeading or burning cause while not increasing processing cost, and Can effectively be solved to burn away the refuse the problem that two brought English pollute by pyrolysis processing.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, art technology Personnel can select according to actual needs.
According to embodiments of the invention, cement kiln synergetic unit 300 has feed(raw material)inlet 301, fuel inlet 302, gives up Gas outlet 303 and cement exit 304, fuel inlet 302 is connected with pyrolytic carbon outlet 206, and is suitable to radiate heat accumulating type The pyrolytic carbon that pipe revolving bed obtains makes cement slurry carry out collaborative process as the fuel of cement kiln synergetic unit, thus Waste gas and cement can be obtained.Inventor finds, is supplied to cement by the pyrolytic carbon obtained by heat accumulation type radiant tube revolving bed Kiln synergetic unit uses as fuel so that limestone, clay matter etc. as between cement slurry occur synergism, Such that it is able to garbage disposal is combined with cement kiln synergetic unit, relative to existing cement kiln synergic processing 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, and then realize the innoxious of organic waste and recycling treatment.
Concrete, with reference to Fig. 2, cement kiln synergetic unit 300 include raw material grinding mill 31, homogenizing storehouse 32, preheater 33, Dore furnace 34, rotary kiln 35, clinker warehouse 36 and fine coal deployment device 37 etc., according to a particular embodiment of the invention, reference Fig. 2, can use at least one in pyrolytic carbon supply to preheater 33, dore furnace 34, rotary kiln 35 as fuel, Cement slurry carries out pulverizing and dried through raw material grinding mill 31, supply successively to homogenizing storehouse 32, preheater 33, dore furnace 34, Rotary kiln 35, clinker warehouse 36 and fine coal deployment device 37 process, and obtain waste gas and cement products.Become for controlling raw material Partial wave is dynamic can increase in-line analyzer at raw material grinding mill, 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 by the organic waste that will obtain after house refuse pretreatment, 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 can be catalyzed and split Solve the pyrolysis oil in gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this part quick lime warp Can supply after pyrogenic processes to subsequent process and use as cement producting material, thus can while not increasing processing cost With the wasting of resources avoiding garbage loading embeading or burning to cause, and can effectively solve to burn away the refuse brought by pyrolysis processing Two English pollute problem, simultaneously using gained pyrolytic carbon supply use as fuel to cement kiln synergetic unit, from And garbage disposal and cement kiln synergetic unit can be combined, relative to existing cement kiln synergic processing side 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, produces The problem that raw 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 is clean Gasifying device 400, combustible gas storage tank 500 and sewage-treatment plant 600.
According to embodiments of the invention, Oil-gas Separation purifier 400 have 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, and suitable In the pyrolysis oil gas that will obtain in heat accumulation type radiant tube revolving bed for carrying out isolation of purified process, such that it is able to isolated pyrolysis Air and heat solution oil and the second sewage.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 Actual conditions during this can be selected by technical staff according to actual needs.
According to embodiments of the invention, combustible gas storage tank 500 has the second combustible gas entrance 501 and the second combustible gas outlet 502, 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 be suitable to obtain pretreatment unit The second sewage that first sewage and Oil-gas Separation purifier obtain carries out purified treatment, such that it is able to obtain treatment fluid.Need Illustrating, the actual conditions employed in this process can be selected by those skilled in the art according to actual needs.
With reference to Fig. 4, according to embodiments of the invention, inorganic refuse outlet 104 is connected with feed(raw material)inlet 301, and be suitable to by The inorganic refuse containing glass, brick and tile and branch etc. of pretreatment unit isolated supplies to cement kiln synergetic unit Substitute For Partial clayey raw material uses, such that it is able to significantly reduce manufacture of cement cost.Concrete, inorganic refuse on the one hand can Substitute For Partial clay raw material, saves cement raw material and puts into, and on the other hand the poisonous and harmful substance in inorganic refuse is through cement Solidification achieves harmless treatment, and wherein, inorganic refuse is of low quality in the 15% of cement entirety raw material.
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 gained To 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, System energy consumption can be significantly reduced.
As it has been described above, the system of process house refuse according to embodiments of the present invention can have selected from least one following advantage:
The system of process house refuse according to embodiments of the present invention uses heat accumulation type radiant tube revolving bed that house refuse is carried out heat Solve, 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 by refuse pyrolysis is combined with cement kiln production line, Take full advantage of the oil of refuse pyrolysis generation, gas, charcoal, the product after refuse pyrolysis is directly utilized, need not sell outward, save Sales section;
The system of process house refuse according to embodiments of the present invention just adds quick lime in pyrolytic process, both plays pyrolysis Catalytic action, can save again the link that later stage cement raw material adds, 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 utilized by cement kiln, Save the raw material required for cement kiln produces;
The system of process house refuse according to embodiments of the present invention relative to original rubbish and cement kiln combined technology, 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, life Rubbish can also process;
The system of process house refuse according to embodiments of the present invention improves the macroeconomic of refuse pyrolysis gasifying process, easily In industrialization promotion.
In another aspect of the invention, the present invention proposes a kind of method processing house refuse.Enforcement according to the present invention Example, 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 Fig. 6, The method of 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, such that it is able to obtain smelly to pretreatment unit Gas, 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, then by garbage grab bucket, heap is filtered After 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 Coming, then sieve through rotary screen, the organic waste obtained supplies to subsequent process after roll crushing crusher machine again Reason.
S200: quick lime, organic waste and foul smell are supplied to heat accumulation type radiant tube revolving bed
According to embodiments of the invention, using the foul smell supply combustion-supporting sky to heat accumulation type radiant tube revolving bed as heat accumulation type radiant tube Gas uses, and provides heat in burning for revolving bed in heat accumulation type radiant tube together with the first combustible gas, by quick lime with have 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 rubbish 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, Qi Zhongtian after pyrolysis The quick lime added with the tar in catalytic pyrolysis pyrolysis oil gas, thus can improve the yield of pyrolysis gas.The heat accumulating type that pyrolysis uses Ringwise, furnace bottom can rotate the burner hearth of radial canal revolving bed continuously, the organic waste obtained after pretreatment and quick lime, Loaded in heat accumulation type radiant tube revolving bed by feeding device, be laid in equably on furnace bottom, layer thickness about 40~800mm, Furnace bottom machine 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, one Conversion zone, two conversion zones and three conversion zones, be finally heated to about 600~900 DEG C and complete pyrolytic reaction, after pyrolysis Pyrolytic carbon is unloaded by pyrolytic carbon outlet outside coming out of the stove, and immediately enters cooling chamber cooling, is pyrolyzed the oil gas multiple pyrolysis oil gas from burner hearth Outlet is discharged.Inventor finds, raw by the organic waste that will obtain after house refuse pretreatment, foul smell and cement raw material Calx supply carries out pyrolysis processing to heat accumulation type radiant tube revolving bed, and quick lime can be with in catalytic pyrolysis gained pyrolysis oil gas Pyrolysis oil, such that it is able to significantly improve the yield of gained pyrolysis gas, and this part quick lime can supply after pyrogenic processes Use as cement producting material to subsequent process, thus garbage loading embeading can be avoided while not increasing processing cost or burn Burn the wasting of resources that causes, and can effectively be solved to burn away the refuse the problem that two brought English pollute by pyrolysis processing.
S300: make cement slurry carry out collaborative process as fuel pyrolytic carbon supply to cement kiln synergetic unit
According to embodiments of the invention, the pyrolytic carbon obtained by heat accumulation type radiant tube revolving bed is as cement kiln synergetic unit Fuel make cement slurry carry out collaborative process, such that it is able to obtain waste gas and cement.Inventor finds, by by accumulation of heat The pyrolytic carbon supply that formula radial canal revolving bed obtains uses as fuel to cement kiln synergetic unit so that limestone, As there is synergism in clay matter etc., such that it is able to garbage disposal had with cement kiln synergetic unit between cement slurry Machine combines, and relative to existing cement kiln synergic processing method, in this application, once cement kiln production line stops production, House refuse can also be pyrolyzed in advance, will not bank up smelly, produces the problem that rubbish can be put nowhere, and then realizes organic waste Innoxious and recycling treatment.According to a particular embodiment of the invention, pyrolytic carbon is supplied to cement kiln synergetic unit On preheater, dore furnace and rotary kiln at least one use as fuel.
The method of process house refuse according to embodiments of the present invention by the organic waste that will obtain after house refuse pretreatment, 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 can be catalyzed and split Solve the pyrolysis oil in gained pyrolysis oil gas, such that it is able to significantly improve the yield of gained pyrolysis gas, and this part quick lime warp Can supply after pyrogenic processes to subsequent process and use as cement producting material, thus can while not increasing processing cost With the wasting of resources avoiding garbage loading embeading or burning to cause, and can effectively solve to burn away the refuse brought by pyrolysis processing Two English pollute problem, simultaneously using gained pyrolytic carbon supply use as fuel to cement kiln synergetic unit, from And garbage disposal and cement kiln synergetic unit can be combined, relative to existing cement kiln synergic processing side 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, produces The problem that raw 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: pyrolysis oil gas supply to Oil-gas Separation purifier is carried out isolation of purified process, and gained pyrolysis gas is supplied Use to heat accumulation type radiant tube revolving bed as combustion gas
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 the supply of gained pyrolysis gas is rotated to heat accumulation type radiant tube Bed uses as combustion gas.Concrete, the pyrolysis oil gas from heat accumulation type radiant tube revolving bed is pyrolyzed through wet dedusting tower, general After the dust carried in oil gas is removed, enter the transverse pipe initial cooler of two parallel operations, enter back into what two parallel connections operated simultaneously Electrical tar precipitator, completes to remove the tar work carried secretly in pyrolysis gas, then by coal gas Roots blower, pyrolysis gas is delivered to dry method Desulfurization process, the gas-liquid separator separates pyrolysis oil got off and circulation pyrolysis water enter mechanization oil-water separation tank, enter at this Row circulation pyrolysis water, pyrolysis oil separating, i.e. isolated pyrolysis oil and sewage.It should be noted that people in the art Actual conditions during this can be selected by member according to actual needs.
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 that pretreatment unit is obtained 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 Need the actual conditions employed in this process is selected.
With reference to Fig. 8, according to embodiments of the invention, the method for described process house refuse farther includes:
S600: carry out collaborative process in the inorganic refuse supply obtained by S100 to cement kiln synergetic unit
According to embodiments of the invention, by the inorganic refuse containing glass, brick and tile and branch etc. of pretreatment unit isolated Supply to Substitute For Partial clayey raw material in cement kiln synergetic unit uses, such that it is able to significantly reduce manufacture of cement cost. Concrete, inorganic refuse on the one hand alternative part clay raw material, save cement raw material and put into, on the other hand inorganic refuse In poisonous and harmful substance achieve harmless treatment through cement solidification effect, wherein, inorganic refuse is of low quality in cement The 15% of overall raw material.
With reference to Fig. 9, according to embodiments of the invention, the method for described process house refuse farther includes:
S700: waste gas supply to the TRT obtained by S300 carries out UTILIZATION OF VESIDUAL HEAT IN, and supplies boiler residual air to cement kiln Raw material grinding mill in synergetic unit
According to embodiments of the invention, waste gas step S300 obtained supply carries out UTILIZATION OF VESIDUAL HEAT IN to TRT, thus can To obtain boiler residual air, and the supply of boiler residual air is used to the raw material grinding mill in cement kiln synergetic unit as dry medium. 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 the most descriptive , and limit the present invention never in any form.
Embodiment
Use the processs house refuse shown in Figure 10 system certain city's house refuse is processed, house refuse one-tenth be grouped into 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 refuse pit into through discharging platform Carrying out heap filter, obtain foul smell (being mainly composed of methane) and contaminant water, the rubbish after then being filtered by heap by garbage grab bucket is sent into In apron feeder, uniform and stable for material is transported on belt feeder by apron feeder with uniform distribution machine, and belt feeder is by rubbish 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 rolling Shaft screen sieves, and 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: foul smell and organic waste, quick lime from rubbish pretreatment unit supply extremely Heat accumulation type radiant tube revolving bed is heated to about 800 DEG C, contained by it under conditions of isolation air in revolving bed pyrolysis oven Organic substance and the volatile matter overwhelming majority separate out, obtain after pyrolysis being pyrolyzed oil gas and two kinds of products of pyrolytic carbon.The storage that pyrolysis uses Ringwise, furnace bottom can rotate the burner hearth of hot type radial canal revolving bed continuously, and the organic waste obtained after pretreatment, by filling Material device loads in heat accumulation type radiant tube revolving bed, is laid in equably on furnace bottom, layer thickness about 700mm, furnace bottom machine 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 800 DEG C and complete pyrolytic reaction, and the pyrolytic carbon after pyrolysis is by being pyrolyzed 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 to water The preheater of stall synergetic unit, dore furnace and rotary kiln use as fuel, from house refuse pretreatment unit Inorganic matter warehouse in the cement plant that inorganic refuse send, delivers on the feed belt of raw material grinding mill after grab bucket feeding, metering, with Raw material enters raw material grinding mill after dispensing to carry out pulverizing and is dried, and can increase online in raw material grinding mill system for controlling material composition fluctuation Analyser.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 gas warp of heat accumulation type radiant tube revolving bed Cross wet dedusting tower, after the dust carried is removed, enter the transverse pipe initial cooler of two parallel operations, then enter in pyrolysis oil gas Enter the electrical tar precipitator that two parallel connections operate simultaneously, complete to remove the tar work carried secretly in pyrolysis gas, then roused 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 machinery by blower fan Change oil-water separation tank, be circulated pyrolysis water, pyrolysis oil separating, i.e. isolated pyrolysis oil and sewage at this, and will divide 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, gained sewage supply in Oil-gas Separation purifier gained sewage and pretreatment unit is filled to sewage disposal Put and process.
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 ", " concrete example ", Or specific features, structure, material or the feature bag that the description of " some examples " etc. means to combine this embodiment or example describes It is contained at least one embodiment or the example of the present invention.In this manual, to the schematic representation of above-mentioned term necessarily It is directed to identical embodiment or example.And, the specific features of description, structure, material or feature can be arbitrary Individual or multiple embodiment 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 combined by art personnel 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 exemplary, Being not considered as limiting the invention, those of ordinary skill in the art within the scope of the invention can be to above-described embodiment It 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 rubbish Rubbish 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 and 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 outlet And cement exit, 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 Outlet and the second outlet of sewer, described pyrolysis oil gas entrance is connected with described pyrolysis oil gas vent;
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 the outlet of described inorganic refuse and described feed(raw material)inlet It is connected.
4. according to the system described in any one of claim 1-3, it is characterised in that the outlet of described pyrolytic carbon 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 described in 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) house refuse supply is carried out pretreatment to described pretreatment unit, in order to obtain foul smell, organic waste, nothing Machine 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 institute State organic waste and carry out pyrolysis processing, obtain being pyrolyzed oil gas and pyrolytic carbon;
(3) cement slurry is made to carry out collaborative place as fuel described pyrolytic carbon supply to described cement kiln synergetic unit Reason, in order to obtain waste gas and cement.
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;
(5) described second sewage that described first sewage step (1) obtained and step (4) obtain supplies to sewage Reason device, in order to obtain treatment fluid.
8. according to the method described in claim 6 or 7, it is characterised in that farther include:
(6) described inorganic refuse supply step (1) obtained carries out described association to described cement kiln synergetic unit With processing.
9. according to the method according to any one of claim 6-8, it is characterised in that the described heat that step (2) is obtained Solve at least one in charcoal supply preheater, dore furnace and rotary kiln to described cement kiln synergetic unit as fuel Use.
10. according to the method according to any one of claim 6-9, it is characterised in that farther include:
(7) described waste gas supply step (3) obtained carries out UTILIZATION OF VESIDUAL HEAT IN to described TRT, in order to obtain boiler Residual air, 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.
CN201610431684.XA 2016-06-16 2016-06-16 Household garbage treatment system and method Pending CN105903752A (en)

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Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007229660A (en) * 2006-03-02 2007-09-13 Sunaoshi Purari Kk Process for treating waste containing vinyl chloride resin
JP2012011299A (en) * 2010-06-30 2012-01-19 Altis:Kk Pyrolyzer, dechlorination treatment apparatus, pyrolysis method and dechlorination 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
CN103626409A (en) * 2013-11-27 2014-03-12 北京建筑材料科学研究总院有限公司 Method and device for treatment in feeding household garbage into cement kiln in three routes
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
CN104006390A (en) * 2014-06-16 2014-08-27 重庆问源环保工程有限公司 Method for generating power through cooperative garbage disposal of cement plant
CN104457289A (en) * 2013-09-24 2015-03-25 安阳市新天河水泥有限责任公司 Method for improving cement production waste heat power generation capacity
CN104550201A (en) * 2015-01-14 2015-04-29 江苏鹏飞集团股份有限公司 Household refuse disposing system with cooperation of cement kiln and method thereof
CN105043115A (en) * 2015-06-25 2015-11-11 中能世华(北京)节能科技有限公司 Cement kiln waste heat power-generation device
CN106077024A (en) * 2016-06-16 2016-11-09 北京神雾环境能源科技集团股份有限公司 Process the system and method for house refuse

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007229660A (en) * 2006-03-02 2007-09-13 Sunaoshi Purari Kk Process for treating waste containing vinyl chloride resin
JP2012011299A (en) * 2010-06-30 2012-01-19 Altis:Kk Pyrolyzer, dechlorination treatment apparatus, pyrolysis method and dechlorination 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
CN104457289A (en) * 2013-09-24 2015-03-25 安阳市新天河水泥有限责任公司 Method for improving cement production waste heat power generation capacity
CN103626409A (en) * 2013-11-27 2014-03-12 北京建筑材料科学研究总院有限公司 Method and device for treatment in feeding household garbage into cement kiln in three routes
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
CN104006390A (en) * 2014-06-16 2014-08-27 重庆问源环保工程有限公司 Method for generating power through cooperative garbage disposal of cement plant
CN104550201A (en) * 2015-01-14 2015-04-29 江苏鹏飞集团股份有限公司 Household refuse disposing system with cooperation of cement kiln and method thereof
CN105043115A (en) * 2015-06-25 2015-11-11 中能世华(北京)节能科技有限公司 Cement kiln waste heat power-generation device
CN106077024A (en) * 2016-06-16 2016-11-09 北京神雾环境能源科技集团股份有限公司 Process the system and method for house refuse

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
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 *

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