CN205664395U - High concentration contains salt organic waste liquid incineration boiler - Google Patents

High concentration contains salt organic waste liquid incineration boiler Download PDF

Info

Publication number
CN205664395U
CN205664395U CN201520852749.9U CN201520852749U CN205664395U CN 205664395 U CN205664395 U CN 205664395U CN 201520852749 U CN201520852749 U CN 201520852749U CN 205664395 U CN205664395 U CN 205664395U
Authority
CN
China
Prior art keywords
chamber
convection current
boiler
current cooling
cooling chamber
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.)
Expired - Fee Related
Application number
CN201520852749.9U
Other languages
Chinese (zh)
Inventor
余传林
何成国
唐义磊
王祺
李鹏飞
郑贺
曹红阳
曹威
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
DALIAN KELIN ENERGY ENGINEERING TECHNOLOGY DEVELOPMENT Co Ltd
Original Assignee
DALIAN KELIN ENERGY ENGINEERING TECHNOLOGY DEVELOPMENT Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by DALIAN KELIN ENERGY ENGINEERING TECHNOLOGY DEVELOPMENT Co Ltd filed Critical DALIAN KELIN ENERGY ENGINEERING TECHNOLOGY DEVELOPMENT Co Ltd
Priority to CN201520852749.9U priority Critical patent/CN205664395U/en
Application granted granted Critical
Publication of CN205664395U publication Critical patent/CN205664395U/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency

Landscapes

  • Gasification And Melting Of Waste (AREA)

Abstract

The utility model discloses a high concentration chemical industry contains salt organic waste liquid incineration boiler, burns through high temperature and realizes with waste heat recovery that the high concentration contains salt organic waste liquid's innoxious, minimizing, the environmental protection of resourceization, energy -conserving requirement. Its structure mainly includes auxiliary combustion ware, waste liquid spray gun, adiabatic furnace combustion chamber, turns to the room, radiation cooling room, radiation water -cooling tube panel, convection current evaporation tube panel, steam pocket, high -temperature economizer, low -level (stack -gas) economizer, ash falling bucket, flue connection expansion joint and brickwork. Adiabatic furnace combustion chamber is applied wall membrane wall by furnace and is enclosed, contains the salt liquid waste incineration, and soluble salt retrieves in the groove. The high temperature flue gas that burns the production gets into adiabatic burning in proper order and turns to room, rapid cooling room, multistage convection current evaporation cooling room, economizer and carry out heat recovery. The utility model discloses have that manufacturing process is simple, easy maintenance, operation safety and stability, trades such as suitable chemical industry, oil refining and papermaking are handled high concentrations and are contained salt organic waste liquid and use widely.

Description

A kind of high concentration salty organic waste liquid burning boiler
Technical field
This utility model relates to a kind of chemical industry, the high concentration salty organic waste liquid of paper industry carries out the environment protection energy-saving equipment of burning disposal and energy recovery, refers more particularly to a kind of high-concentration chemical industry organic waste liquid containing salt burning boiler.This utility model relates to a kind of chemical industry, oil refining, the high concentration salty organic waste liquid of paper industry carry out the environment protection energy-saving equipment of burning disposal and energy recovery, refers more particularly to a kind of high concentration salty organic waste liquid burning boiler.
Background technology
In recent years, fast development along with industries such as chemical industry, oil refining, papermaking, in its production process, often produce substantial amounts of high-concentration chemical industry salty organic waste liquid, these waste liquids are discharged in the Nature containing a large amount of non-biodegradable Organic substances and high concentration salty organic waste liquid, necessarily to environment, destroy ecological environment, infringement health, thus find a kind for the treatment of technology reasonable, effective, thus reduce the pollution to environment of this waste liquid, promote that industry value chain is significant.At present, industrial wastes processing method is mainly used biodegradation, method to deep under ground high-pressure injection and burning.The way of domestic usual employing burning disposal, burns toxic waste liquid by incinerator, makes waste liquid be decomposed into non-toxic gas in combustion, enter air.Why high concentration salty organic waste liquid burning boiler becomes the process difficult problem that environmental protection is burned, and also a major reason is: burn the alkaline metal salt containing a large amount of low melting points in the high-temperature flue gas generated.These materials all produce strong corrosiveness to furnace lining and heat-transfer surface, furnace lining can be caused to be burned or heating surface fouling and clogging, and cause system to be not normally functioning.
Analyzing after deliberation, the fusing point of pure sodium salt is at 801 DEG C-894 DEG C, but its fusing point to be reduced to 600 DEG C-750 DEG C under combinational environment, though fusing point following sodium salt bonding, under this state, sodium salt has fragility, and corresponding soot blower can be used to be removed.The melting temperature 600 DEG C-750 DEG C that the flue-gas temperature entering convection bank falls farther below sodium salt under combinational environment to this end, to try one's best just is conducive to boiler safety reliability service.
Patent CN103047659A proposes a kind of burning process processing high concentration salty organic waste liquid and burning boiler, including descending adiabatic furnace, multi-stage irradiation cooling chamber, convection heat-exchange chamber, soot blower, soda pop fairlead and drum, but the liquid waste incineration boiler described in this patent has the disadvantage in that (1) descending adiabatic furnace volume from top to bottom is excessive, for ensureing combustion temperature in hearth, a large amount of auxiliary fuel must be consumed, thus result in treatment cost of waste liquor and increase;(2) if arrange between descending adiabatic furnace and the first radiant cooling room by dry tablet number vertically with tilt deflector, this deflector easily cause vertically with tilt the molten state inorganic salt blocking that deflector is incinerated in rear flue gas, cause the equipment cannot be properly functioning.(3) block without smoke wall between descending adiabatic furnace and the first radiant cooling room, uncovered turn of descending adiabatic furnace is to the first radiant cooling room, due to heat radiation effect, the burning of descending adiabatic furnace is played negative effect by the first radiant cooling room, it is difficult to make the burning of descending adiabatic furnace to reach a high temperature burning stage, unless consumed a large amount of auxiliary fuel just can ensure that the incineration temperature of descending adiabatic furnace, if strengthening auxiliary fuel consumption, exhaust gas volumn is made again to increase, flue gas flow rate increases therewith, the most not only cause tail temperature too high, the most detrimentally flue gas flow rate increase causes flue gas to take away a large amount of fused salt to rear portion multi-stage irradiation cooling chamber, cause multi-stage irradiation cooling chamber salification serious, harm safe and reliable operation.If do not strengthen auxiliary fuel consumption will cause descending adiabatic furnace temperature of lower it is difficult to ensure that, slag tap difficulty, even result in slag-drip opening blocking cannot deslagging;(4) heating surface is not arranged in multi-stage irradiation cooling chamber, on the one hand due to the physical property feature of fused salt could be less in adhesiveness when the temperature of fused salt is well below the fusing point of fused salt solid granulates, but flue gas carries the most tiny fused salt granule, by on the furnace wall wall adhering to multi-stage irradiation cooling chamber what radiant cooling room especially front along journey, cause multi-stage irradiation cooling chamber heating surface pickup to affect radiation cooling effectiveness, and cause ash bucket bottom the blocking of multi-stage irradiation cooling chamber and multi-stage irradiation cooling chamber cannot normally work because fused salt blocking is tied.On the other hand the heating surface of fused salt pickup radiant cooling room causes radiant heat transfer to weaken, and reduces waste heat recovery efficiency, causes burning boiler bulky, increases construction investment;(5) this burning boiler only arranges the convection current tube panel of parallel baffled at low-temperature space, and heat-transfer effect is excessively poor, thus causes high fume temperature, and boiler thermal output is low.(6) on the right side of descending adiabatic furnace bottom, uncovered liquid state slag discharging device is set, this liquid state slag discharging device is difficult to reliability service, on the one hand the viscosity of fused salt is the least along with the viscosity of the highest fused salt of temperature when temperature is far above the fusing point of fused salt, but the temperature that this apparatus structure feature determines descending adiabatic furnace is difficult to the fusing point far above fused salt, so auxiliary fuel consumption must be strengthened when running could meet the requirement of slag tap with the temperature improving descending adiabatic furnace;The most uncovered liquid state slag discharging device is to atmospheric radiation heat exchange, and this process is very fast, causes fused salt easily to stick on the pipeline of liquid state slag discharging device because of cooling, starts local stoppages, and gradually wholly liquid state slag-draining device cannot be properly functioning.
Utility model content
nullDefect for above-mentioned prior art,Low especially for high concentration salty organic waste liquid fused salt fusing point、Strong to refractory corrosion、Cementability is stronger、The characteristics such as waste heat recovery difficulty,In conjunction with flue gas characteristic,A kind of resistance to sodium salt is provided to corrode、Slag tap is smooth、Waste heat recovery efficiency is high、Rationally effectively eliminate or avoid fused salt to body of heater and the cementability of boiler heating surface、The energy-efficient organic waste liquid containing salt burning boiler that exhaust gas temperature is low,Take appropriate measures from following starting point: (1)、Reduce insulated combustion chamber height,Increase insulated combustion chamber cross-sectional area,In certain insulated combustion chamber volume,Velocity of flue gas reduces,Salty organic waste liquid realizes evaporation in insulated combustion chamber、It is dried、Organic compound combustion with burn、Inorganic salt solid-state phase changes are the processes such as liquid,The increase of combustor cross-sectional area causes flue gas flow rate to reduce,Be conducive to relying on gravity solid-state in flue gas and liquid inorganic salt to be deposited to bottom insulated combustion chamber,Plus insulated combustion chamber lower needle, solid-state and the liquid inorganic salt of bottom deposit are reheated,The solid-state and the liquid inorganic salt that make deposition are completely reformed into liquid,Essential condition and sufficient condition is created for realizing liquid salt discharge.(2), enter insulated combustion chamber in view of high concentration salty organic waste liquid spraying to burn, fused salt is in combustion on the one hand in fine granularity state, easily brought into rear pole miscellaneous part by flue gas, on the other hand fused salt local temperature in combustion is too high causes little granular solid or liquid fused salt to become gaseous state mutually, unavoidably brought into rear pole miscellaneous part by flue gas, once gaseous state or liquid fused salt bring rear pole miscellaneous part into, the hugest to its harm, one quench chamber must be set specially gaseous state or liquid fused salt are quenched to the solid-state to rear pole miscellaneous part non-hazardous, for this, this patent arranges a bigger quench chamber being equiped with a large amount of chilling membrane panel after insulated combustion chamber, gaseous state or liquid fused salt are quenched to the solid-state to rear pole miscellaneous part non-hazardous.null(3)、In view of the relation between insulated combustion chamber and quench chamber,I.e. insulated combustion chamber wants high-temp combustion,Quench chamber to cool down rapidly,If without hiding cigarette wall between insulated combustion chamber and quench chamber,So heat of quench chamber direct radiation absorption insulated combustion chamber,Reduce the temperature of insulated combustion chamber,It is unfavorable for that the liquid realizing inorganic salt in salty organic waste liquid is got rid of outside stove,For this,This patent arranges between insulated combustion chamber and quench chamber and internally tilts the burner hearth flue gas of certain angle and turn to screening cigarette wall,This screening cigarette wall i.e. plays the reduction quench chamber rotating jet flow to insulated combustion chamber、Improve insulated combustion chamber bottom temp effect,Be conducive to again the saliferous melt substance in flue gas to separate to flow to be formed in a big fused salt groove bottom insulated combustion chamber and adiabatic combustion reversal chamber along adiabatic combustion reversal chamber wall,Reheat burner reheating by fused salt to be in a liquid state completely,The liquid being conducive to inorganic salt is got rid of outside stove.(4), a bigger fused salt groove is formed bottom insulated combustion chamber and bottom adiabatic combustion reversal chamber, the side wall installing fused salt of fused salt groove reheats burner, the fused salt of deposition fused salt groove is reheated so that it is sufficiently achieve liquid, it is simple to trickle and implement the purpose of slag tap.(5), whole fused salt groove tilts bottom concentration to bottom center, bottom center at fused salt groove arranges a special fused salt overflow mechanism specially, liquid saline solution flows to fused salt overflow mechanism projection in fused salt groove, the centre of fused salt overflow mechanism projection arranges a fused salt spout hole according to flow rate of molten salt, this fused salt spout hole is much smaller than the internal diameter of overflow cylinder, guarantee that fused salt does not adhere to along journey on the internal face of overflow cylinder, cause the discharge of liquid fused salt smooth and easy;(6), convection current cooling chamber after quench chamber is arranged convection current evaporation tube panel, on the one hand the most further quench chamber about 500 DEG C flue gases out are lowered the temperature, on the other hand multistage convection current cooling chamber is set, flue gas turns to dependence inertia-gravity effect to be separated by solid salt grain through repeatedly 180 °, fall collection recycling in the bottom ash bucket of convection current cooling chamber, 3rd arranges convection current evaporation tube panel in convection current cooling chambers at different levels, make flue gas and convection current evaporation tube panel collision, realize solid salt grain and run out of steam and separate because of further cooling and the collision of convection current evaporation tube panel.(7), economizer tube bank is set in convection current cooling chamber rear portion (positions of flue-gas temperature≤250 DEG C), on the one hand flue gas transversal flow economizer tube bank, make flue gas and economizer tube bank collision to greatest extent, realize further cooling and collision that solid salt grain restrains because of economizer to run out of steam and separate, on the other hand transversal flow obtain economizer tube bank compared with the low temperature convection current of parallel baffled evaporation tube panel can with heat transfer coefficient will the most several times, can more effectively save heating surface material and realize reducing further smog discharge temperature and improve boiler thermal output.(8), the flue gas produced in view of high concentration salty organic waste liquid burning has stronger etching characteristic, before boiler feedwater enters low-level (stack-gas) economizer, feedwater is first imported feed water preheater, saturated or the superheated steam produced by boiler is heated to above more than the dew point temperature of acid gas in flue gas to the feedwater entering low-level (stack-gas) economizer, the most just import low-level (stack-gas) economizer, not only achieve used heat makes full use of the purpose reaching energy-conservation, it is also possible to the metal material being required for costliness achieves the purpose of consumption reduction manufacturing low-level (stack-gas) economizer.
For realizing object above, by the following technical solutions: a kind of high concentration salty organic waste liquid burning boiler, comprise insulated combustion chamber, adiabatic combustion reversal chamber, quench chamber, convection current cooling chamber I, convection current cooling chamber II, convection current cooling chamber III, expansion joint, high temperature section economizer, middle-temperature section economizer, low-temperature zone economizer and boiler flue gas outlet, it is characterized in that, described insulated combustion chamber, adiabatic combustion reversal chamber, quench chamber, convection current cooling chamber I, convection current cooling chamber II, convection current cooling chamber III, expansion joint, high temperature section economizer, middle-temperature section economizer, low-temperature zone economizer and boiler flue gas outlet are sequentially communicated;
Described insulated combustion chamber, adiabatic combustion reversal chamber, quench chamber, convection current cooling chamber I, convection current cooling chamber II, the membrane wall furnace wall of convection current cooling chamber III all introduce boiler-steam dome by the soda pop fairlead of its top header, by connecting pipeline from the boiler common downcomer introducing boiler water of boiler-steam dome to the header of its underpart, separately constitute respective natural convection loop;
Described insulated combustion chamber and adiabatic combustion reversal chamber side towards the fire furnace wall all use pink fused alumina refractory concrete cast resistant to salt corrosion to form.
Described quench chamber, convection current cooling chamber I, convection current cooling chamber II, convection current cooling chamber III is equiped with chilling membrane panel respectively, convection current evaporation tube panel I, convection current evaporation tube panel II, convection current evaporation tube panel III, described all tube panels are each provided with top header and bottom header, top header is connected with boiler-steam dome, bottom header is connected with boiler common downcomer, all tube panels connect and boiler-steam dome each via pipeline, boiler common downcomer composition natural convection loop, boiler feedwater sequentially enters low-temperature zone economizer by boiler feed pump, middle-temperature section economizer, high temperature section economizer, boiler feedwater is introduced boiler-steam dome by the pipeline being connected with high temperature section economizer by boiler-steam dome.
Described insulated combustion chamber, adiabatic combustion reversal chamber hide integral combustion room, one, cigarette walled city by fin panel casing furnace wall and adiabatic combustion reversal chamber, some atomizing lances are arranged at insulated combustion chamber crown wall position or at three side wall topmosts of insulated combustion chamber, the high concentration salty organic waste liquid being sprayed into atomization by atomizing lance enters insulated combustion chamber, it is to arrange several auxiliary burners by layer on three furnace walls on insulated combustion chamber top, at insulated combustion chamber, layout some boiler maintenances manhole of adiabatic combustion reversal chamber furnace wall.
Described insulated combustion chamber, adiabatic combustion reversal chamber hide cigarette walled by fin panel casing furnace wall with adiabatic combustion reversal chamber and become the bottom, integral combustion room of to be equiped with fused salt overflow mechanism, exporting to fused salt cool down in fused salt cooling bath and reclaim, fused salt overflow mechanism is made up of fused salt spout hole, overflow cylinder, overflow ducts.
Described insulated combustion chamber, adiabatic combustion reversal chamber hide cigarette walled by fin panel casing furnace wall with adiabatic combustion reversal chamber and become an integral combustion room, hide cigarette wall by adiabatic combustion reversal chamber and are separated with quench chamber described integral combustion room.
Described quench chamber is arranged chilling membrane panel, chilling membrane panel is provided with top header and bottom header, top header is connected with boiler-steam dome, bottom header is connected with boiler common downcomer, is connected and boiler-steam dome, boiler common downcomer composition natural convection loop by pipeline.
Described convection current cooling chamber I, convection current cooling chamber II, convection current cooling chamber III are all to be surrounded by fin panel casing furnace wall, and convection current cooling chamber I, convection current cooling chamber II, the bottom of convection current cooling chamber III are provided with ash dropping hopper.
Boiler feedwater is introduced into feed water preheater heating, the steam utilizing boiler to produce imports low-temperature zone economizer after boiler feedwater heating is reached more than more than the dew point corrosion temperature of acid gas in flue gas, then middle-temperature section economizer, high temperature section economizer are sequentially entered, import to, in boiler-steam dome, boiler be supplied water by the hot water after three grades of economizers by pipeline.Exhaust steam after boiler deoxidizing method water is heated by feed water preheater imports oxygen-eliminating device, on the one hand heating deaerated water gives deoxygenation to water in oxygen-eliminating device, on the other hand exhaust steam is to be absorbed heat by the softening water through deoxygenation to generate, and can be sent directly into oxygen-eliminating device and be recycled.
This utility model beneficial effect: breach traditional liquid waste incineration and the split of energy recovery or integral structure, make liquid waste incineration system simpler, perfect, reliable, be substantially reduced high concentration salty organic waste liquid burning disposal cost;High concentration salty organic waste liquid burning boiler structure the most of the present utility model: the first, adapt to high concentration salty organic waste liquid and burn to be fully achieved the environment protecting that organic principle thoroughly destroys by fire;The second, high saliferous high-temperature flue gas and the energy recovery requirement of high dust-laden high-temperature flue gas are adapted to;3rd, can also reclaim the inorganic salt after high concentration salty organic waste liquid burns or other dust continue with to realize the feature of utilization of waste as resource, meeting environmental protection, under energy-conservation, utilization of waste as resource these three requires, equipment can safe and reliable, stable operation;4th, this utility model also has the features such as manufacturing process is simple, easy to maintenance;5th, this utility model can also be promoted the use of in burned waste gas or waste liquid, waste gas burning disposal simultaneously.
Accompanying drawing explanation
Fig. 1 is structural representation of the present utility model
Fig. 2 is the partial enlarged drawing of fused salt overflow mechanism bottom insulated combustion chamber
Fig. 3 is the system schematic of feed water preheater
As shown in the figure: 1, insulated combustion chamber;2, pink fused alumina castable refractory furnace wall;3, fin panel casing furnace wall;4, heat-insulation layer;5, auxiliary burner;6, liquid waste spray gun;7, boiler soda pop tedge;8, boiler-steam dome;9, boiler common downcomer;10, convection current cooling chamber I;11, convection current evaporation tube panel I;12, convection current cooling chamber II;13, convection current evaporation tube panel II;14, convection current cooling chamber III;15, convection current evaporation tube panel III;16, expansion joint;17, high temperature section economizer;18, middle-temperature section economizer;19, low-temperature zone economizer;20, boiler flue gas outlet;21, fused salt overflow mechanism;22, adiabatic combustion reversal chamber;23, adiabatic combustion reversal chamber hides cigarette wall;24, quench chamber;25, chilling membrane panel;26, ash dropping hopper;27, fused salt cooling bath;28, steam sootblower interface;29, inspection manhole;30, insulated combustion chamber bottom refractory layer;31, fused salt spout hole;32, overflow cylinder;33, overflow ducts;34, fused salt reheats burner;35, feed water preheater;36, fused salt groove.
Detailed description of the invention
Embodiment
A kind of high-concentration chemical industry organic waste liquid containing salt burning boiler as shown in Figure 1, its direction of arrow represents that liquid waste incineration high-temperature flue gas moves towards;Its structure specifically includes that its structure specifically includes that insulated combustion chamber (1), adiabatic combustion reversal chamber (22), adiabatic combustion reversal chamber hides cigarette wall (23), quench chamber (24), chilling membrane panel (25), convection current cooling chamber I(10), convection current evaporation tube panel I(11), convection current cooling chamber II(12), convection current evaporation tube panel II(13), convection current cooling chamber III(14), convection current evaporation tube panel III(15), expansion joint (16), high temperature section economizer (17), middle-temperature section economizer (18), low-temperature zone economizer (19), boiler flue gas outlet (20), fused salt cooling bath (27), fused salt reheats burner (34), feed water preheater (35).
Insulated combustion chamber (1) is surrounded by fin panel casing furnace wall (3), insulated combustion chamber (1) side towards the fire uses pink fused alumina castable refractory furnace wall (2), insulated combustion chamber (1) outside is that alumina silicate fiber felt is as heat-insulation layer (4), many atomizing lances are arranged at insulated combustion chamber (1) crown wall position or at that is three side wall topmosts of insulated combustion chamber (1) crown wall position down certain altitude, the high concentration salty organic waste liquid being sprayed into atomization by atomizing lance enters insulated combustion chamber (1), it is to arrange multiple auxiliary burners (5) by layer on three furnace walls on insulated combustion chamber (1) top, in insulated combustion chamber (1), the different parts of adiabatic combustion reversal chamber (22) fin panel casing furnace wall (3) arranges necessary boiler maintenance manhole (29).
Quench chamber (24), convection current cooling chamber I(10), convection current evaporation tube panel I(11), convection current cooling chamber II(12), convection current evaporation tube panel II(13), convection current cooling chamber III(14) all surrounded by fin panel casing furnace wall (3).Convection current cooling chamber I(10) in arrange convection current evaporation tube panel I(11), convection current cooling chamber II(12) in arrange convection current evaporation tube panel II(13), convection current cooling chamber III(14) in convection current evaporation tube panel III(15 is set), convection current cooling chamber I(10) and convection current cooling chamber II(12) bottom is provided with ash dropping hopper (26).Insulated combustion chamber (1), quench chamber (24), convection current cooling chamber I(10), convection current cooling chamber II(12), convection current cooling chamber III(14), expansion joint (16), high temperature section economizer (17), middle-temperature section economizer (18), low-temperature zone economizer (19) and exhanst gas outlet (20) be sequentially communicated, insulated combustion chamber (1), quench chamber (24), convection current cooling chamber I(10), convection current cooling chamber II(12), convection current cooling chamber III(14) be connected to boiler-steam dome (8) by soda pop tedge (4) respectively.Insulated combustion chamber (1) and quench chamber (24) connectivity part are adiabatic combustion reversal chamber (22), adiabatic combustion reversal chamber (22) is hidden cigarette wall (23) by adiabatic combustion reversal chamber and hides every surrounding with quench chamber (24), insulated combustion chamber (1) and adiabatic combustion reversal chamber (22) bottom one bigger fused salt groove (36) of composition, fused salt groove (36) bottom centre position is provided with fused salt overflow mechanism (21), the salification being deposited in fused salt groove (36) reheats burner (34) combustion heating through the fused salt being arranged in fused salt groove (36) side wall position, make the salification being deposited in fused salt groove (36) become liquid mutually because of high temperature and pass through to arrive in fused salt cooling bath (27) outside fused salt overflow mechanism (21) boss center fused salt spout hole (31) outflow stove.
nullGaseous fuel or liquid fuel spray into burning in insulated combustion chamber (1) by auxiliary burner (5),When fire box temperature reaches more than 1100 DEG C,Pending high concentration salty organic waste liquid carries out high temperature incineration in being sprayed into insulated combustion chamber (1) by liquid waste spray gun (6),High concentration salty organic waste liquid passes through high temperature evaporation in insulated combustion chamber (1)、Heating、Cracking、The harmful organic substance in waste liquid can be effectively removed after burning process,The inorganic salt of molten condition relies on gravity solid-state in flue gas and liquid inorganic salt to be deposited in insulated combustion chamber (1) and adiabatic combustion reversal chamber (22) bottom one bigger fused salt groove (36) of composition,Burner (34) combustion heating is reheated through being arranged in the fused salt at fused salt groove (36) side wall position,The solid-state and the liquid inorganic salt that make deposition in fused salt groove (36) are completely reformed into liquid,Flowed out by fused salt overflow mechanism (21) boss center fused salt spout hole (31) and arrive in fused salt cooling bath (27) outside stove.nullThe fused salt becoming gaseous state mutually is downwardly into quench chamber (24) through adiabatic combustion reversal chamber (22) leading of adiabatic combustion reversal chamber screening cigarette wall (23),Adding heat convection by the fin panel casing furnace wall (3) at quench chamber (24) surrounding and top and the radiation of chilling membrane panel (25) makes flue gas drastically cool to about 500 DEG C,The fused salt becoming gaseous state mutually becomes solid-state mutually,Part deposition relies on gravity to drop back in fused salt groove (36),Another part fine particle sequentially enters convection current cooling chamber I(10 under the carrying of flue gas)、Convection current cooling chamber II(12)、Convection current cooling chamber III(14),On the one hand the surrounding of convection current cooling chamber and the fin panel casing furnace wall (3) at top and convection current is relied on to evaporate tube panel I(11 in three grades of convection current cooling chambers)、Convection current evaporation tube panel II(13)、Convection current evaporation tube panel III(15) radiation add heat convection and make flue gas drastically cool to about 250 DEG C,On the other hand fine inorganic salt particle evaporates tube panel I(11 with convection current)、Convection current evaporation tube panel II(13)、Convection current evaporation tube panel III(15) collide and through convection current cooling chamber I(10)、Convection current cooling chamber II(12)、Convection current cooling chamber III(14) three times 180 ° turn to dependence inertia-gravity effect solid salt grain is separated,Fall collection recycling in the bottom ash bucket of convection current cooling chamber.
High temperature section economizer (17), middle-temperature section economizer (18), low-temperature zone economizer (19) convection bank heating surface is entered when flue-gas temperature is reduced to 250 DEG C of next coming in order, now the saliferous dust in flue gas no longer has stickiness, is easily removed by soot blower soot blowing.
In quench chamber (24), convection current cooling chamber I(10), convection current cooling chamber II(12), convection current cooling chamber III(14) the middle chilling membrane panel (25) arranged, convection current evaporation tube panel I(11), convection current evaporation tube panel II(13), convection current evaporation tube panel III(15) all use membrane wall pattern water-cooled tube panel structure, the sodium salt that cohesiveness can be avoided stronger adheres on metal wall, inorganic salt under molten condition adheres on membrane wall, can be cooled down further on membrane wall, an aspect is formed on inorganic salt under molten condition and the metal wall of membrane wall abutting edge, deposition relies on when reaching to a certain degree gravity to come off this aspect by nature, fall in fused salt groove (36) and ash dropping hopper (26).
The feedwater of high concentration salty organic waste liquid burning boiler initially enters feed water preheater (35), saturated or the superheated steam utilizing high concentration salty organic waste liquid burning boiler to produce imports low-temperature zone economizer (19) after feedwater heating is reached more than more than the dew point corrosion temperature of acid gas in flue gas, imported in boiler-steam dome (8) by steam-water pipe afterwards then in turn through low-temperature zone economizer (19), middle-temperature section economizer (18), high temperature section economizer (17), boiler is supplied water.Exhaust steam after boiler deoxidizing method water is heated by feed water preheater (35) imports oxygen-eliminating device.
Water in boiler-steam dome (8) is assigned in each heating surface by boiler common downcomer (9), via radiation with convection current evaporating heating surface heat exchange after, soda pop mixture enters boiler-steam dome (8) by each heating surface soda pop tedge (7), through steam-water separation in boiler-steam dome (8), the saturated vapor output heat supply user of generation uses.Salty organic waste liquid has the most not only carried out innoxious, minimizing, utilization of waste as resource processes; also reclaim it and burn the heat energy produced; achieve the environmental protection of organic waste liquid burning, energy-conservation and utilization of resources requirement, not only save the energy but also be conducive to the protection of atmospheric environment.

Claims (7)

  1. null1. a high concentration salty organic waste liquid burning boiler,Comprise insulated combustion chamber (1)、Adiabatic combustion reversal chamber (22)、Quench chamber (24)、Convection current cooling chamber I(10)、Convection current cooling chamber II(12)、Convection current cooling chamber III(14)、Expansion joint (16)、High temperature section economizer (17)、Middle-temperature section economizer (18)、Low-temperature zone economizer (19) and boiler flue gas outlet (20),It is characterized in that,Described insulated combustion chamber (1)、Adiabatic combustion reversal chamber (22)、Quench chamber (24)、Convection current cooling chamber I(10)、Convection current cooling chamber II(12)、Convection current cooling chamber III(14)、Expansion joint (16)、High temperature section economizer (17)、Middle-temperature section economizer (18)、Low-temperature zone economizer (19) and boiler flue gas outlet (20) are sequentially communicated;
    Described insulated combustion chamber (1), adiabatic combustion reversal chamber (22), quench chamber (24), convection current cooling chamber I(10), convection current cooling chamber II(12), convection current cooling chamber III(14) membrane wall furnace wall all introduce boiler-steam dome (8) by the soda pop fairlead of its top header, by connecting pipeline from boiler common downcomer (9) the introducing boiler water of boiler-steam dome (8) to the header of its underpart, separately constitute respective natural convection loop;
    Described insulated combustion chamber (1) and adiabatic combustion reversal chamber (22) side towards the fire furnace wall all use pink fused alumina refractory concrete cast resistant to salt corrosion to form.
  2. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that, in quench chamber (24), convection current cooling chamber I(10), convection current cooling chamber II(13), convection current cooling chamber III(14) in be equiped with chilling membrane panel (25) respectively, convection current evaporation tube panel I(11), convection current evaporation tube panel II(13), convection current evaporation tube panel III(15), described all tube panels are each provided with top header and bottom header, top header is connected with boiler-steam dome (8), bottom header is connected with boiler common downcomer (9), all tube panels connect and boiler-steam dome (8) each via pipeline, boiler common downcomer (9) composition natural convection loop.
  3. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that, insulated combustion chamber (1), adiabatic combustion reversal chamber (22) hides one integral combustion room, cigarette wall (23) besieged city by fin panel casing furnace wall (3) and adiabatic combustion reversal chamber, some atomizing lances are arranged at insulated combustion chamber (1) crown wall position or at (1) three side wall topmost of insulated combustion chamber, it is to arrange several auxiliary burners (5) by layer on three furnace walls on insulated combustion chamber (1) top, in insulated combustion chamber (1), the layout some boiler maintenances manhole (29) of adiabatic combustion reversal chamber (22) furnace wall.
  4. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that: the bottom, integral combustion room that insulated combustion chamber (1), adiabatic combustion reversal chamber (22) surround by fin panel casing furnace wall (3) and adiabatic combustion reversal chamber screening cigarette wall (23) is equiped with fused salt overflow mechanism (21), and fused salt overflow mechanism (21) is made up of fused salt spout hole (31), overflow cylinder (32), overflow ducts (33).
  5. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that, insulated combustion chamber (1), adiabatic combustion reversal chamber (22) hide cigarette wall (23) by fin panel casing furnace wall (3) and adiabatic combustion reversal chamber and surround an integral combustion room, hide cigarette wall (23) by adiabatic combustion reversal chamber and are separated with quench chamber (24) described integral combustion room.
  6. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that, chilling membrane panel (25) is arranged in quench chamber (24), chilling membrane panel (25) is provided with top header and bottom header, top header is connected with boiler-steam dome (8), bottom header is connected with boiler common downcomer (9), is connected and boiler-steam dome (8), boiler common downcomer (9) composition natural convection loop by pipeline.
  7. A kind of high concentration salty organic waste liquid burning boiler the most according to claim 1, it is characterized in that, described convection current cooling chamber I(10), convection current cooling chamber II(13), convection current cooling chamber III(14) be all to be surrounded by fin panel casing furnace wall (3), convection current cooling chamber I(10), convection current cooling chamber II(13), convection current cooling chamber III(14) bottom be provided with ash dropping hopper (26).
CN201520852749.9U 2015-10-30 2015-10-30 High concentration contains salt organic waste liquid incineration boiler Expired - Fee Related CN205664395U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201520852749.9U CN205664395U (en) 2015-10-30 2015-10-30 High concentration contains salt organic waste liquid incineration boiler

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201520852749.9U CN205664395U (en) 2015-10-30 2015-10-30 High concentration contains salt organic waste liquid incineration boiler

Publications (1)

Publication Number Publication Date
CN205664395U true CN205664395U (en) 2016-10-26

Family

ID=57162331

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201520852749.9U Expired - Fee Related CN205664395U (en) 2015-10-30 2015-10-30 High concentration contains salt organic waste liquid incineration boiler

Country Status (1)

Country Link
CN (1) CN205664395U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105240861A (en) * 2015-10-30 2016-01-13 大连科林能源工程技术开发有限公司 Incineration boiler for high-concentration salty organic waste liquid

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105240861A (en) * 2015-10-30 2016-01-13 大连科林能源工程技术开发有限公司 Incineration boiler for high-concentration salty organic waste liquid
CN105240861B (en) * 2015-10-30 2017-11-07 大连科林能源工程技术开发有限公司 A kind of high concentration salty organic waste liquid burning boiler

Similar Documents

Publication Publication Date Title
CN105240861B (en) A kind of high concentration salty organic waste liquid burning boiler
CN104764025B (en) Waste liquid incineration boiler of recycling smoke adherence protection
CN100526716C (en) Plasma medical refuse burning methods
CN109458623B (en) High-salt-content high-chlorine-content organic waste liquid incineration environment-friendly energy-saving discharge system
WO2022082889A1 (en) Novel integrated system for online coupling of hazardous waste combustion and plasma melting
CN102588980B (en) Incineration boiler for saline waste liquid
CN103591591B (en) Saponification waste liquid burning and alkali recovery boiler
CN105605543B (en) A kind of high dust-laden highly corrosive waste heat boiler of metallurgy industry high temperature
CN109838794A (en) A kind of water-cooling jacket incinerator and method handling salt bearing liquid wastes and exhaust gas
CN102168857B (en) High-concentration saliferous organic waste liquid incinerator and incineration technique
CN104676606A (en) Innocent treatment method for acrylic acid and ester waste liquid thereof
CN102788355B (en) Turbulent-style hazardous waste pyrolysis incinerator
CN115371061B (en) High-concentration salt-containing organic waste liquid incineration device and incineration molten slag separation and recovery process
CN109519938A (en) A kind of sulfur-bearing organic waste liquid containing salt burning energy conservation and environmental protection exhaust system
JP2009510383A (en) Steam generating boiler from flue gas under optimum conditions
CN214406092U (en) Environment-friendly incineration boiler suitable for low-calorific-value dangerous waste liquid
CN109974014A (en) A kind for the treatment of method for high-salinity wastewater of propylene oxide/styrene combined production device
CN205664395U (en) High concentration contains salt organic waste liquid incineration boiler
CN204534605U (en) The liquid waste incineration boiler of the adherent protection of a kind of flue gas recycled
CN202074532U (en) High concentration salt bearing organic waste liquid incinerator
CN209445382U (en) A kind of sulfur-bearing organic waste liquid containing salt burning energy conservation and environmental protection exhaust system
CN213930955U (en) Waste heat boiler capable of matching with waste incineration device
CN212777392U (en) Contain salt waste liquid incineration disposal system
CN204786429U (en) Living beings rubbish combustion system
CN104949131A (en) Biomass garbage combustion system and method

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20161026

Termination date: 20201030

CF01 Termination of patent right due to non-payment of annual fee