CN205897157U - A process systems that is used for cement kiln to deal with in coordination hazardous waste - Google Patents

A process systems that is used for cement kiln to deal with in coordination hazardous waste Download PDF

Info

Publication number
CN205897157U
CN205897157U CN201620865742.5U CN201620865742U CN205897157U CN 205897157 U CN205897157 U CN 205897157U CN 201620865742 U CN201620865742 U CN 201620865742U CN 205897157 U CN205897157 U CN 205897157U
Authority
CN
China
Prior art keywords
waste
kiln
cement kiln
dangerous
incineration
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201620865742.5U
Other languages
Chinese (zh)
Inventor
蔡珠华
邝焯荣
陈宗达
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.)
Guangzhou Weigang Environment Technology Co Ltd
Original Assignee
Guangzhou Weigang Environment Technology 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 Guangzhou Weigang Environment Technology Co Ltd filed Critical Guangzhou Weigang Environment Technology Co Ltd
Priority to CN201620865742.5U priority Critical patent/CN205897157U/en
Application granted granted Critical
Publication of CN205897157U publication Critical patent/CN205897157U/en
Active 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/34Indirect CO2mitigation, i.e. by acting on non CO2directly related matters of the process, e.g. pre-heating or heat recovery

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

The utility model discloses a process systems that is used for cement kiln to deal with in coordination hazardous waste, including the storage of dangerous waste incineration kiln system, solid waste and feed system, waste liquid storage and feed system, oxygen boosting preparation system, the bypass is leaked informaton and waste heat recovery system and cement kiln system. The utility model discloses a hazardous waste is dealt with in coordination to the outer kiln process water stall of kiln, the wastes material burns through the bypass, incorporate the cement kiln after the homogenization again into, the kind of system to the wastes material has been improved, the form, the adaptability of calorific value and composition, reduce in coordination with disposal of wastes to the stable influence of cement kiln system's operating mode, therefore can improve disposal of wastes's ability in coordination by a wide margin, gain better environmental protection and economic benefits, furthermore, the dore furnace is introduced to the high temperature flue gas that produces behind the dangerous waste incineration in the dangerous waste incineration kiln, the high heating value waste liquid directly spouts into the dore furnace, can be for a large amount of fire coal of dore furnace saving.

Description

A kind of process system for cement kiln synergic processing hazardous waste
Technical field
This utility model belongs to the hazardous waste processing technology field in field of environment protection;More particularly, to one kind is used for water The process system of stall cooperative disposal hazardous waste.
Background technology
Fast development with national social economy;The yield of solid dangerous waste also sharply increases;If not had Effect processes and will have a strong impact on the sustainable development of social economy.2004;National solid dangerous waste yield is 1,200,000,000 tons;Than Last year increases by 20%;Wherein annual about 30,000,000 tons of the poisonous and harmful hazardous waste producing of industrial and mining establishment;These hazardous wastes have Be corrosive, flammable, reactivity, acute toxicity and Leaching;It is the primary pollution source of air, water source, soil.China is every Year rubbish rate of increase is constantly being increased with more than 10% speed;So numerous waste residue, waste material;Accumulate over a long period not pregnancy ceased Go out;If disposal can not suitably be dissolved;Severe contamination certainly will be caused to the ecological environment of the whole society;Loss economically is particularly Huge.Noxious substance in the solid dangerous waste that cannot properly dispose in a large number;Pollute earth's surface and subsoil water;Pollute sky Gas;Seriously threaten the physical and mental health of its people;If this phenomenon cannot be contained in time;Consequence is very serious;This becomes one Extremely urgent, problem demanding prompt solution.
Contain this phenomenon for timely;The national discharge to these hazardous waste materials is renovated.A series of phases The waste treatment device answered also just arises at the historic moment.At present;Adopting cement kiln synergic processing hazardous waste most of enterprise institution more. Theory and practice both domestic and external has proved that using cement kiln synergic processing garbage be innoxious, minimizing and disposal of resources The important technology approach of hazardous waste and domestic waste;It is also that cost degradation extensive disposal the important of above-mentioned waste is arranged Apply.
China utilizes the practice of cement kiln synergic processing hazardous waste as follows:
The nineties in (a) last century;The practice that hazardous waste is put in cement kiln coexistence is initiated in Shanghai Wan An cement plant at home;
B () Beijing cement plant nineteen ninety-five starts the examination burning practice that hazardous waste disposed by cement kiln;The whole nation the has been built in research and development Article one, the environmental protection demonstration line of common disposal of commercial (dangerous) waste;
C () Huaxin Cement Factory assume responsibility for the domestic demonstrative project putting pesticide garbage first using cement kiln coexistence;2007 That Hubei Province was taken in~2009 years gives up in about more than 1650 interior ton solids containing 5 kinds of high-toxic pesticide wastes such as Bayer 71628, parathion Thing carries out coprocessing.
But above-mentioned cement kiln synergic processing process is only the productive prospecting from cement plant;It is cement round how Factory saves raw materials and fuel and reducing energy consumption material consumption is carried out.The toss area of hazardous waste mainly has kiln hood, kiln tail smoke-box, rises cigarette Road, dore furnace etc..In view of the multiformity of the production requirement of cement kiln and hazardous waste species and complexity;Alternative danger Waste species is simultaneously few;And careful pretreatment before adding, must be carried out.
Therefore;This collaborative technique promotion effect is unsatisfactory;The advantage of cement kiln synergic processing hazardous waste also cannot Give full play of;After the adding equipment in a lot of cement plants builds up;Due to hazardous waste species and composition aspect cannot be adapted to Change;Cannot realize normally adding;Adding equipment is substantially at idle state;Equipment capital cannot normally reclaim.
Utility model content
In order to overcome the deficiencies in the prior art;The purpose of this utility model is to provide one kind to be used for cement kiln synergic processing The process system of hazardous waste, the flue gas after burning is introduced cement CIU, can strengthen water after cement kiln synergic processing The adaptability of mud production system, extension is suitable for the hazardous waste species of cement kiln synergic processing.
The purpose of this utility model employs the following technical solutions realization:
A kind of process system for cement kiln synergic processing hazardous waste,
Including dangerous waste incineration kiln system, solid waste storage and feed system, waste liquid storage and feed system, oxygen-enriched Preparation system, bypass and residual neat recovering system and quality coal in cement kiln systems;
The solid material outfan of solid waste storage and feed system accesses the solidss of dangerous waste incineration kiln system Material input;
Waste liquid storage and the liquid material outfan liquid material with dangerous waste incineration kiln system respectively of feed system Input, the liquid material input connection of quality coal in cement kiln systems;
In the gas output end of oxygen-enriched preparation system, quality coal in cement kiln systems, the gas output end of tertiary-air pipe all accesses dangerous giving up Thing burns the gas input of kiln system;
Waste gas after dangerous waste incineration kiln system burns is passed through in quality coal in cement kiln systems;
The gas output end of quality coal in cement kiln systems introduces bypass and residual neat recovering system, the gas output of quality coal in cement kiln systems Terminate the gas input into bypass and residual neat recovering system;The gas output end of bypass and residual neat recovering system connects Enter the gas input of quality coal in cement kiln systems.
Preferably, also include bootstrap system, in quality coal in cement kiln systems, the gas output end of tertiary-air pipe accesses waste heat profit With the gas input of system, the gas input of the gas output end access dangerous waste incineration kiln system of bootstrap system End.
Preferably, dangerous waste incineration kiln system includes dangerous waste incineration kiln, waste-liquor burner, drawing-in device, solid Waste feeding chamber and dragveyer, drawing-in device is arranged on solid waste feeding chamber side and connects with it, and waste-liquor burner is solid Be connected to dangerous waste incineration kiln and connect with it, solid waste feeding chamber be arranged on dangerous waste incineration kiln side and with danger Connection in incineration of waste kiln, the dragveyer for incineration residue excretion is fixedly mounted on dangerous waste incineration kiln side.
Preferably, the method for operation of dangerous waste incineration kiln system be reverse-flow operation, lime-ash formula burn.
Preferably, solid waste storage and feed system include solid waste pond, diafiltration liquid pool, diafiltration liquid pump, grab bucket, driving, Hopper, feeding machine, the first elevator and metering feed bin;Driving, can be along solid waste pond length side across the fixed installation of solid waste pond To moving freely;Grab bucket can be stretched up and down, is fixed in driving;Feeding machine is used for material and conveys, and is arranged on the lower section of driving; Hopper is fixedly mounted on feeding machine, and metering feed bin is arranged on below feeding machine one end away from solid waste pond, metering feed bin Discharging opening is connected with dangerous waste incineration kiln system, and the first hoist installation is in solid waste pond near the side of metering feed bin, diafiltration Liquid pool is arranged at the side in solid waste pond, and the diafiltration liquid pump extracting percolate is arranged on percolate at the bottom of pond portion.
Preferably, waste liquid storage and feed system include high heating value waste tank, low heat value waste tank, provisional waste liquid Bucket, the first filter, waste drains pump, the second filter, low heat value waste liquid feeding pump, agitator, the 3rd filter, high heating value waste liquid Feeding pump and high heating value waste liquid heater, high heating value waste tank, low heat value waste tank are all by the first filter, waste drains pump Connect with provisional waste liquid barrel, low heat value waste tank is burnt by the second filter, low heat value waste liquid feeding pump and hazardous waste Firing system connectivity, agitator is arranged on inside high heating value waste tank, and high heating value waste tank passes through the 3rd filter, hyperpyrexia Value waste liquid feeding pump, high heating value waste liquid heater are connected with dangerous waste incineration kiln system.
Preferably, oxygen-enriched preparation system includes adsorption tower, aerator, bottom of towe switching valve, tower top switching valve, oxygen equilibrium Tank, vacuum pump and denitrogen acoustic filter, are provided with inlet filter at blower inlet, aerator passes through bottom of towe switching valve and absorption Tower connects, and multiple adsorption towers are arranged in order, and oxygen equilibrium tank is passed through tower top switching valve and connected with absorption top of tower, denitrogen acoustic filter Connect with absorption tower bottom by bottom of towe switching valve, vacuum pump, the outlet side of oxygen equilibrium tank and dangerous waste incineration kiln system Air intake vent connection.
Preferably, bypass and residual neat recovering system include for generate electricity the first waste heat boiler, the first cyclone dust removal Device, sack cleaner, blower fan, conveying worm, the second elevator and kiln ash feed bin, the gas output end of quality coal in cement kiln systems and the The air intake vent connection of one cyclone dust extractor, the air outlet of the first cyclone dust extractor is connected with the air intake vent of the first waste heat boiler, cloth The air intake vent of bag dust collector is connected with the air outlet of the first waste heat boiler, and blower fan accesses the air outlet of sack cleaner, spiral transferring The outlet sending machine is connected with the entrance of the second elevator, and the outlet of the second elevator is connected with the entrance of kiln ash feed bin, kiln ash material Storehouse pass through the second elevator, conveying worm respectively with the first waste heat boiler, the first cyclone dust extractor, sack cleaner bottom Connection.
Preferably, bootstrap system includes the second waste heat boiler, the second cyclone dust extractor and the air-introduced machine for generating electricity, Second cyclone dust extractor is arranged at the air intake vent of the second waste heat boiler, and air-introduced machine is arranged on the air outlet of the second waste heat boiler Place.
Preferably, quality coal in cement kiln systems includes cement kiln, dore furnace and desulfurizing tower/chimney, and cement kiln is connected with dore furnace;Water The tertiary-air pipe of stall is connected with dangerous waste incineration kiln system, and dangerous waste incineration kiln system is connected with dore furnace;Cement kiln Kiln tail smoke-box connect with bypass and residual neat recovering system, bypass and residual neat recovering system are with desulfurizing tower/chimney even Logical.
Compared to existing technology;The beneficial effects of the utility model are:
This utility model, with brand-new thinking, is jumped out the pattern of original cement kiln synergic processing hazardous waste, is being followed While the productive prospecting of cement plant, with brand-new pattern cooperative disposal hazardous waste, do not use in the past directly by hazardous waste It is added to the mode of cement CIU, but using the outer firer's skill cement kiln synergic processing hazardous waste of kiln, waste is through side It is incorporated to cement kiln again after road burning, homogenizing, improves the species to waste for the system, the adaptability of form, calorific value and composition, reduce The impact to quality coal in cement kiln systems stable conditions for the cooperative disposal waste, thus the ability of cooperative disposal waste can be greatly improved, take Obtain more preferable environmental protection and economic benefit, additionally, the high-temperature flue gas producing after dangerous waste incineration in dangerous waste incineration kiln introduce Dore furnace, high heating value waste liquid is injected directly into dore furnace, can save substantial amounts of fire coal for dore furnace.
Brief description
Fig. 1 is system schematic of the present utility model.
Fig. 2 is dangerous waste incineration kiln system schematic diagram.
Fig. 3 is solid waste storage and feed system schematic diagram.
Fig. 4 is waste liquid storage and feed system schematic diagram.
Fig. 5 is oxygen-enriched preparation system schematic diagram.
Fig. 6 is bypass and residual neat recovering system schematic diagram.
In figure: 10, dangerous waste incineration kiln system;100th, dangerous waste incineration kiln;101st, waste-liquor burner;102nd, feeding Device;103rd, solid waste feeding chamber;104th, dragveyer;20th, solid waste storage and feed system;200th, solid waste pond;201、 Diafiltration liquid pool;202nd, it is percolated liquid pump;203rd, grab bucket;204th, drive a vehicle;205th, hopper;206th, feeding machine;207th, the first elevator; 208th, measure feed bin;30th, waste liquid storage and feed system;300a, high heating value waste tank;300b, low heat value waste tank; 301st, provisional waste liquid barrel;302nd, the first filter;303rd, waste drains pump;304th, the second filter;305th, low heat value waste liquid feeding Pump;306th, agitator;307th, the 3rd filter;308th, high heating value waste liquid feeding pump;309th, high heating value waste liquid heater;40th, rich Oxygen preparation system;400th, adsorption tower;401st, inlet filter;402nd, aerator;403rd, bottom of towe switching valve;404th, tower top switching Valve;405th, oxygen equilibrium tank;406th, vacuum pump;407th, denitrogen acoustic filter;50th, bypass and residual neat recovering system;500th, One waste heat boiler;501st, the first cyclone dust extractor;502nd, sack cleaner;503rd, blower fan;504th, conveying worm;505th, second Elevator;506th, kiln ash feed bin;60th, bootstrap system;600th, the second waste heat boiler;601st, the second cyclone dust extractor;602、 Air-introduced machine;70th, quality coal in cement kiln systems;700th, cement kiln;701st, dore furnace;702nd, desulfurizing tower/chimney.
Specific embodiment
Below;In conjunction with accompanying drawing and specific embodiment;This utility model is described further:
Process system for cement kiln synergic processing hazardous waste as shown in Figure 1, including dangerous waste incineration kiln system System 10, solid waste storage and feed system 20, waste liquid storage and feed system 30, oxygen-enriched preparation system 40, bypass and Residual neat recovering system 50 and quality coal in cement kiln systems 70;
The solid material outfan of solid waste storage and feed system 20 accesses consolidating of dangerous waste incineration kiln system 10 Body material input;
Waste liquid storage and the liquid material outfan liquid with dangerous waste incineration kiln system 10 respectively of feed system 30 Material input, the liquid material input connection of quality coal in cement kiln systems 70;
In the gas output end of oxygen-enriched preparation system 40, quality coal in cement kiln systems 70, the gas output end of tertiary-air pipe all accesses danger The gas input of dangerous incineration of waste kiln system 10;
Waste gas after dangerous waste incineration kiln system 10 burns is passed through in quality coal in cement kiln systems 70;
The gas output end of quality coal in cement kiln systems 70 introduces bypass and residual neat recovering system 50, the gas of quality coal in cement kiln systems 70 Body outfan accesses the gas input of bypass and residual neat recovering system 50;Bypass and the gas of residual neat recovering system 50 Body outfan accesses the gas input of quality coal in cement kiln systems 70.
Solid waste storage and feed system 20 can take into account solid waste deposit and solid waste automatic transport Feeding, depositing of solid waste can be realized by various ways, such as solid waste pond, storage casing, centralized stores station etc., and solid gives up The automatic transport of thing can be realized by the following manner: belt conveyor, plate-type feeding, elevator, conveying worm etc., common Solid mechanical feed such as automatic transport of coal dust, clay, Ore etc..
Waste liquid storage and feed system 30 can take into account depositing and pipeline feeding of waste liquid, and waste liquid is deposited can be by giving up Liquid pool, pressure pan, bucket etc. are realized, the common in the following manner of mechanical feed of waste liquid: pumping takes pipeline, helical feed Machine, pressure transmission etc., existing common device is waste drains pump.
As shown in Fig. 1~2, the solid waste from solid waste storage and feed system 20 is delivered to dangerous waste incineration In kiln system 10, burning disposal after being dried by the high-temperature flue gas in dangerous waste incineration kiln system 10.
Spray into from waste liquid storage and the low heat value waste liquid of feed system 30, provisional waste liquid and part high heating value waste liquid In dangerous waste incineration kiln system 10, hot-air combustion-supporting under, moisture all evaporates, and Organic substance is thoroughly destroyed by fire, is formed high Warm flue gas and inorganic residues.
Spray into burning in quality coal in cement kiln systems 70 from the remainder high heating value waste liquid of waste liquid storage and feed system 30, enter One step reduces the coal-fired consumption in cement plant.
Oxygen rich gas from oxygen-enriched preparation system 40 is mixed with the hot-air of tertiary-air pipe in quality coal in cement kiln systems 70 Input dangerous waste incineration kiln system 10 afterwards.
The high-temperature flue gas that dangerous waste incineration kiln system 10 produces after burning enter quality coal in cement kiln systems 70, using cement kiln system Distinctive alkaline environment in system 70, the harmful substance in absorption flue gas, finally it is cleaned rear flue gas and produce with quality coal in cement kiln systems 70 Flue gas qualified discharge together;The incineration residue that dangerous waste incineration kiln system 10 produces after burning is delivered to water after water quench cooling Raw Material System dispensing in stall system 70, enters quality coal in cement kiln systems 70 with raw material and burns, and forms grog, residue harmful Composition is melted admittedly in clinker.
Extract the high-temp waste gas input bypass being full of volatile component on a small quantity and waste heat returns from quality coal in cement kiln systems 70 Receipts system 50, carries out sufficient heat exchange, and the volatile component in waste gas is condensate in dust surface, row up to standard after gas removing dust Put, and collect waste residue kiln ash feeding quality coal in cement kiln systems 70 and recycle, grind cement as mixing material;It is big that heat exchange produces Calorimetric can be used for generating electricity.
As shown in figure 1, the present embodiment also includes bootstrap system 60, in quality coal in cement kiln systems 70, the gas of tertiary-air pipe is defeated Go out the gas input terminating into bootstrap system 60, the gas output end of bootstrap system 60 accesses dangerous waste incineration The gas input of kiln system 10.
In quality coal in cement kiln systems 70, the hot air temperature of tertiary-air pipe is often beyond 1000 DEG C, based on temperature adjustability with Economic feasibility, one bypass of setting between the tertiary-air pipe in quality coal in cement kiln systems 70 and dangerous waste incineration kiln system 10, In quality coal in cement kiln systems 70, through bypass input bootstrap system 60, hot-air is in UTILIZATION OF VESIDUAL HEAT IN system for the hot-air of tertiary-air pipe Mix with the oxygen rich gas from oxygen-enriched preparation system 40 after fully carrying out heat exchange cooling in system 60, input dangerous waste incineration Kiln system 10.And a large amount of heat energy absorbing in bootstrap system 60 are converted into high-temperature vapor, can be used for generating set and generate electricity. Bootstrap system 60 greatly strengthen the motility adjusting the hot air temperature entering dangerous waste incineration kiln system 10, enters danger Dangerous incineration of waste kiln system 10 hot air temperature can flexible between 150 DEG C to 1100 DEG C according to actual needs.
Further, as shown in Fig. 2 dangerous waste incineration kiln system 10 includes dangerous waste incineration kiln 100, waste-liquor burner 101st, drawing-in device 102, solid waste feeding chamber 103 and dragveyer 104, drawing-in device 102 is arranged on solid waste feeding chamber 103 sides simultaneously connect with it, and waste-liquor burner 101 is fixed in dangerous waste incineration kiln 100 and connects with it, solid waste Feeding chamber 103 is arranged on dangerous waste incineration kiln 100 side and connects, for incineration residue with dangerous waste incineration kiln 100 The dragveyer 104 of excretion is fixedly mounted on dangerous waste incineration kiln 100 side.
Solid waste from solid waste storage and feed system 20 pushes solid waste feeding chamber by drawing-in device 102 103;Fired by waste liquid from waste liquid storage and the low heat value waste liquid of feed system 30, provisional waste liquid and part high heating value waste liquid Burner 101 sprays into dangerous waste incineration kiln 100;From the oxygen rich gas of oxygen-enriched preparation system 40, mixing is from tertiary-air pipe Hot-air, enters dangerous waste incineration kiln 100 together.
From waste liquid storage and the low heat value waste liquid of feed system 30, provisional waste liquid and part high heating value waste liquid by giving up Liquid burner 101 sprays into dangerous waste incineration kiln 100.Low heat value waste liquid, provisional waste liquid and part high heating value waste liquid are in warm Air combustion-supporting under, moisture all evaporates, and Organic substance is thoroughly destroyed by fire, forms high-temperature flue gas and inorganic residues.
The high-temperature flue gas producing after dangerous waste incineration enter quality coal in cement kiln systems 70 through solid waste feeding chamber 103, utilize Distinctive alkaline environment in quality coal in cement kiln systems 70, the harmful substance in absorption flue gas, finally it is cleaned rear flue gas with cement kiln 700 Flue gas qualified discharge together.The incineration residue of dangerous waste incineration kiln 100 is discharged by dragveyer 104 after water quench cooling, sends into life Material system dispensing, enters in quality coal in cement kiln systems 70 with raw material and burns, form grog, the harmful components of residue are melted admittedly in water In mud grog.
Remaining most of high heating value waste liquid from waste liquid storage and feed system 30 sprays into cement by waste-liquor burner 101 Burn in kiln system 70, replace fired coal combustion, reduce the coal-fired consumption in cement plant in quality coal in cement kiln systems 70 further.
Further, as shown in figure 1, the method for operation of dangerous waste incineration kiln system 10 is reverse-flow operation, lime-ash formula burns Burn.
The dangerous waste disposal mode that the present embodiment preferably employs is reverse-flow operation, lime-ash formula is burned.Give up from solid The solid waste of thing storage and feed system 20 feeds from solid waste feeding chamber 103 entrance, goes out with dangerous waste incineration kiln 100 The high-temperature flue gas contact coming, after being dried by high-temperature flue gas, falls into dangerous waste incineration kiln 100.Hazardous waste burns in hazardous waste In firing 100, rolling is advanced, and inversely goes with gas, constantly contacts with fresh hot air, Organic substance is thoroughly destroyed by fire, moisture All evaporate, form high-temperature flue gas and inorganic residues.
Further, as shown in figure 3, solid waste storage and feed system 20 include solid waste pond 200, diafiltration liquid pool 201, ooze Filtrate pump 202, grab bucket 203, driving 204, hopper 205, feeding machine 206, the first elevator 207 and metering feed bin 208;Driving 204 fixedly mount across solid waste pond 200, can move freely along solid waste pond 200 length direction;Grab bucket 203 can be stretched up and down, It is fixed in driving 204;Feeding machine 206 is used for material and conveys, and is arranged on the lower section of driving 204;Hopper 205 is fixedly mounted on On feeding machine 206, metering feed bin 208 is arranged on below feeding machine 206 one end away from solid waste pond 200, measures going out of feed bin 208 Material mouth is connected with dangerous waste incineration kiln system 10, and the first elevator 207 is arranged on solid waste pond 200 near metering feed bin 208 Side, diafiltration liquid pool 201 is arranged at the side in solid waste pond 200, and the diafiltration liquid pump 202 extracting percolate is arranged on diafiltration liquid pool 201 bottoms.
Solid waste, leaves in solid waste pond 200 in solid waste pond 200 after compatibility, by grab bucket 203 and driving 204 feeding In hopper 205, deliver to metering feed bin 208 through feeding machine 206, because metering feed bin 208 bottom is mounted with metering device, work as meter After in amount feed bin 208, waste reaches constant weight, the valve plate of metering feed bin 208 lower section automatically opens up, and solid waste falls, and enters Dangerous waste incineration kiln system 10.
Semi-solid (pulpous state or paste) waste and waste in bulk deliver to metering feed bin 208 through the first elevator 207.Metering material Storehouse 208 bottom is mounted with metering device, after in metering feed bin 208, waste reaches constant weight, the valve of metering feed bin 208 lower section Plate automatically opens up, and semi-solid (pulpous state or paste) waste and waste in bulk fall, and enters dangerous waste incineration kiln system 10.
The leachate collection that solid waste is formed, in diafiltration liquid pool 201, is pumped to percolate bucket by diafiltration liquid pump 202 Interior, then be transported in waste liquid storage and feed system 30, it is done and disposes further.
The waste gas of solid waste storage and feed system 20 generation passes through existing cement plant existing device grate-cooler and cools down wind Grate-cooler sent into by machine, enters quality coal in cement kiln systems 70, and the harmful components in waste gas are thoroughly destroyed by fire in cement production process.
Further, as shown in figure 4, waste liquid storage and feed system 30 include high heating value waste tank 300a, low heat value is given up Liquid storage tank 300b, provisional waste liquid barrel 301, the first filter 302, waste drains pump 303, the second filter 304, low heat value waste liquid are fed Material pump 305, agitator 306, the 3rd filter 307, high heating value waste liquid feeding pump 308 and high heating value waste liquid heater 309, hyperpyrexia Value waste tank 300a, low heat value waste tank 300b are all by the first filter 302, waste drains pump 303 and provisional waste liquid barrel 301 connections, low heat value waste tank 300b passes through the second filter 304, low heat value waste liquid feeding pump 305 and dangerous waste incineration Kiln system 10 connects, and agitator 306 is arranged on inside high heating value waste tank 300a, and high heating value waste tank 300a passes through the 3rd Filter 307, high heating value waste liquid feeding pump 308, high heating value waste liquid heater 309 are connected with dangerous waste incineration kiln system 10.
Waste liquid is transported to waste liquid tank field by waste liquid tank car, after rapid comparison chemical examination, the difference according to calorific value and the compatibility Difference, high heating value waste tank 300a specified or low heat value waste liquid are pumped to by the first filter 302 and waste drains pump 303 Storage tank 300b.
Low heat value waste liquid in low heat value waste tank 300b is through the second filter 304 and low heat value waste liquid feeding pump 305 Conveying, enters dangerous waste incineration kiln system 10.
Because high heating value waste liquid is different with the property of low heat value waste liquid, its storage mode and mode of movement are slightly not yet With.It is mounted with agitator 306 in high heating value waste tank 300a.Agitator 306 is by the hyperpyrexia in high heating value waste tank 300a Value waste liquid is sufficiently stirred for, and forms homogeneous liquid, and the high heating value waste liquid after homogenizing is fed through the 3rd filter 307 and high heating value waste liquid Material pump 308 is sent into high heating value waste liquid heater 309 and is heated, and increases its mobility.High heating value waste liquid fraction after heating It is transported to burning in dangerous waste incineration kiln system 10;Remaining major part is sent to burning, replacement portion in quality coal in cement kiln systems 70 Divide fire coal, reduce the coal-fired consumption in cement plant.High heating value waste liquid heater 309 heats thermal source used and comes from UTILIZATION OF VESIDUAL HEAT IN system System 60, the condensate water circulatory after heat exchange utilizes.
Determine after rapid comparison chemical examination and be not suitable for into the special waste liquid of tank and come from the tight of social accident Anxious waste liquid injects in provisional waste liquid barrel 301, is fed directly to hazardous waste by the first filter 302 and waste drains pump 303 and burns Carry out burn processing in firing system 10.
Further, as shown in figure 5, oxygen-enriched preparation system 40 include adsorption tower 400, aerator 402, bottom of towe switching valve 403, Tower top switching valve 404, oxygen equilibrium tank 405, vacuum pump 406 and denitrogen acoustic filter 407, aerator 402 air inlet be provided with into Make a slip of the tongue filter 401, aerator 402 is connected with adsorption tower 400 by bottom of towe switching valve 403, and multiple adsorption towers 400 are arranged in order, Oxygen equilibrium tank 405 is connected with adsorption tower 400 top by tower top switching valve 404, and denitrogen acoustic filter 407 passes through bottom of towe switching valve 403rd, vacuum pump 406 is connected with adsorption tower 400 bottom, the outlet side of oxygen equilibrium tank 405 and dangerous waste incineration kiln system 10 Air intake vent connection.
After air through inlets filter 401 removes impurity, blasted equipped with multiple Special adsorbent (molecules by aerator 402 Sieve etc.) adsorption tower 400 bottom, most n2、co2、so2、h2O and a small amount of o2It is adsorbed by adsorbent in adsorption tower 400, and Most of o2Then discharge through tower top switching valve 404 from tower top through bed, form oxygen rich gas, enter oxygen equilibrium tank 405.
After the adsorbent in adsorption tower 400 a certain in oxygen-enriched preparation system 40 reaches dynamic saturation, oxygen-enriched preparation system 40 are automatically stopped and blast air to this adsorption tower 400, direct air to another adsorption tower 400 by bottom of towe switching valve 403, continue Manufacture oxygen rich gas.After former adsorption tower 400 stops air inlet, oxygen-enriched preparation system 40 automatic desorption process, open vacuum pump 406, by absorption n on the sorbent2、co2、so2、h2O etc. desorbs, and is entered big after denitrogen acoustic filter 407 noise reduction Gas.
Oxygen rich gas in oxygen equilibrium tank 405 is sent to the gas input of dangerous waste incineration kiln system 10, with From after the hot-air mixing of tertiary-air pipe, enter dangerous waste incineration kiln system 10.
Further, as shown in fig. 6, bypass and residual neat recovering system 50 include the first waste heat boiler for generating electricity 500th, the first cyclone dust extractor 501, sack cleaner 502, blower fan 503, conveying worm 504, the second elevator 505 and kiln ash Feed bin 506, the gas output end of quality coal in cement kiln systems 70 is connected with the air intake vent of the first cyclone dust extractor 501, the first cyclone dust removal The air outlet of device 501 is connected with the air intake vent of the first waste heat boiler 500, the air intake vent of sack cleaner 502 and the first waste heat pot The air outlet connection of stove 500, blower fan 503 accesses the air outlet of sack cleaner 502, the outlet of conveying worm 504 and second The entrance connection of elevator 505, the outlet of the second elevator 505 is connected with the entrance of kiln ash feed bin 506, and kiln ash feed bin 506 leads to Cross the second elevator 505, conveying worm 504 respectively with the first waste heat boiler 500, the first cyclone dust extractor 501, bag-type dust The bottom connection of device 502.
The bypass gas that kiln tail smoke-box bleed off passage from quality coal in cement kiln systems 70 is extracted out, is mixed with appropriate cold air Afterwards, enter the first cyclone dust extractor 501 and carry out rough dusting, the flue gas through rough dusting enters the first waste heat boiler 500 to be carried out Sufficiently heat exchange, temperature is down to 150 DEG C about, then through bagroom dust removal process, delivers to quality coal in cement kiln systems by blower fan 503 70 process, enter air.The heat energy that first waste heat boiler 500 absorbs is converted into high-temperature steam, delivers to generating set, is converted into electricity Energy.
The kiln ash collected is delivered to kiln ash feed bin 506 through conveying worm 504 and the second elevator 505, then turns It is transported to quality coal in cement kiln systems 70, grinds cement as mixing material, fully recycle.
Further, bootstrap system 60 include for generate electricity the second waste heat boiler 600, the second cyclone dust extractor 601 With air-introduced machine 602, the second cyclone dust extractor 601 is arranged at the air intake vent of the second waste heat boiler 600, and air-introduced machine 602 is arranged on The air outlet of the second waste heat boiler 600.
From the hot-air of tertiary-air pipe, after the second cyclone dust extractor 601 rough dusting, enter the second waste heat boiler 600, after sufficient heat exchange, then sent in dangerous waste incineration kiln 100 by air-introduced machine 602.High-temperature hot air is in the second waste heat Boiler 600 carries out heat exchange, and a large amount of heat energy distributing are absorbed by the second waste heat boiler 600, and the heat energy of absorption is converted into height Warm steam, delivers to generating set, is converted into electric energy.
Further, quality coal in cement kiln systems 70 includes cement kiln 700, dore furnace 701 and desulfurizing tower/chimney 702, cement kiln 700 Connect with dore furnace 701;The tertiary-air pipe of cement kiln 700 is connected with dangerous waste incineration kiln system 10, dangerous waste incineration kiln System 10 is connected with dore furnace 701;The kiln tail smoke-box of cement kiln 700 is connected with bypass and residual neat recovering system 50, bypass Leak informaton and residual neat recovering system 50 is connected with desulfurizing tower/chimney 702.
Dangerous waste incineration kiln 100 and the separate operation of cement kiln 700, are assisted using the outer firer's skill cement kiln 700 of kiln With disposing hazardous waste, waste is incorporated to cement kiln 700 after bypass burning, homogenizing again.The high temperature producing after dangerous waste incineration Flue gas enters dore furnace 701, using distinctive alkaline environment in dore furnace 701, adsorbs the harmful substance in flue gas, finally net After change, flue gas is with cement kiln 700 flue gas qualified discharge.Incineration residue is discharged by dragveyer 104 after water quench cooling, sends into life Material system dispensing, enters cement kiln 700 with raw material and burns, and forms grog, and the harmful components of residue are melted ripe in cement admittedly In material.
Spray into dore furnace 701 from remaining most of high heating value waste liquid of waste liquid storage and feed system 30, burning substitutes Fire coal, reduces the coal-fired consumption in cement plant further.
To one skilled in the art;Can technical scheme as described above and design;Make other various Corresponding change and deformation;And all these change and deformation all should belong to the protection of this utility model claim Within the scope of.

Claims (10)

1. a kind of process system for cement kiln synergic processing hazardous waste;It is characterized in that: include dangerous waste incineration kiln System, solid waste storage and feed system, waste liquid storage and feed system, oxygen-enriched preparation system, bypass and waste heat return Receipts system and quality coal in cement kiln systems;
The solid material that the solid material outfan of solid waste storage and feed system accesses dangerous waste incineration kiln system is defeated Enter end;
The liquid material outfan of waste liquid storage and feed system is inputted with the liquid material of dangerous waste incineration kiln system respectively End, the liquid material input connection of quality coal in cement kiln systems;
In the gas output end of oxygen-enriched preparation system, quality coal in cement kiln systems, the gas output end of tertiary-air pipe all accesses hazardous waste and burns The gas input of firing system;
Waste gas after dangerous waste incineration kiln system burns is passed through in quality coal in cement kiln systems;
The gas output end of quality coal in cement kiln systems introduces bypass and residual neat recovering system, and the gas output end of quality coal in cement kiln systems connects Enter the gas input of bypass and residual neat recovering system;The gas output end of bypass and residual neat recovering system accesses water The gas input of stall system.
2. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: also wrap Include bootstrap system, in quality coal in cement kiln systems, the gas output end of tertiary-air pipe accesses the gas input of bootstrap system, The gas output end of bootstrap system accesses the gas input of dangerous waste incineration kiln system.
3. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: dangerous Incineration of waste kiln system includes dangerous waste incineration kiln, waste-liquor burner, drawing-in device, solid waste feeding chamber and dragveyer, Drawing-in device is arranged on solid waste feeding chamber side and connects with it, and waste-liquor burner is fixed in dangerous waste incineration kiln simultaneously Connect with it, solid waste feeding chamber is arranged on dangerous waste incineration kiln side and connects with dangerous waste incineration kiln, use Dragveyer in incineration residue excretion is fixedly mounted on dangerous waste incineration kiln side.
4. the process system for cement kiln synergic processing hazardous waste according to claim 3;It is characterized in that: dangerous The method of operation of incineration of waste kiln system is reverse-flow operation, lime-ash formula is burned.
5. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: solid Waste storage and feed system include solid waste pond, diafiltration liquid pool, diafiltration liquid pump, grab bucket, driving, hopper, feeding machine, first carry The machine of liter and metering feed bin;Driving, across the fixed installation of solid waste pond, can move freely along solid waste pond length direction;Grab bucket can be gone up Lower flexible, it is fixed in driving;Feeding machine is used for material and conveys, and is arranged on the lower section of driving;Hopper is fixedly mounted on feeding On machine, metering feed bin is arranged on below feeding machine one end away from solid waste pond, measures discharging opening and the dangerous waste incineration of feed bin Kiln system connects, and in solid waste pond near the side of metering feed bin, diafiltration liquid pool is arranged at the one of solid waste pond to the first hoist installation Side, the diafiltration liquid pump extracting percolate is arranged on percolate at the bottom of pond portion.
6. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: waste liquid Storage and feed system include high heating value waste tank, low heat value waste tank, provisional waste liquid barrel, the first filter, waste liquid Pump, the second filter, low heat value waste liquid feeding pump, agitator, the 3rd filter, high heating value waste liquid feeding pump and high heating value waste liquid Heater, high heating value waste tank, low heat value waste tank are all by the first filter, waste drains pump with provisional waste liquid barrel even Logical, low heat value waste tank passes through the second filter, low heat value waste liquid feeding pump is connected with dangerous waste incineration kiln system, stirring Device is arranged on inside high heating value waste tank, and high heating value waste tank passes through the 3rd filter, high heating value waste liquid feeding pump, hyperpyrexia Value waste liquid heater is connected with dangerous waste incineration kiln system.
7. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: oxygen-enriched Preparation system includes adsorption tower, aerator, bottom of towe switching valve, tower top switching valve, oxygen equilibrium tank, vacuum pump and denitrogen and eliminates the noise Device, is provided with inlet filter at blower inlet, aerator is connected with adsorption tower by bottom of towe switching valve, multiple adsorption towers according to Secondary arrangement, oxygen equilibrium tank is passed through tower top switching valve and is connected with absorption top of tower, and denitrogen acoustic filter passes through bottom of towe switching valve, vacuum Pump is connected with absorption tower bottom, and the outlet side of oxygen equilibrium tank is connected with the air intake vent of dangerous waste incineration kiln system.
8. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: bypass Leak informaton and residual neat recovering system include for generate electricity the first waste heat boiler, the first cyclone dust extractor, sack cleaner, blower fan, Conveying worm, the second elevator and kiln ash feed bin, the inlet air of the gas output end of quality coal in cement kiln systems and the first cyclone dust extractor Mouthful connection, the air outlet of the first cyclone dust extractor connects with the air intake vent of the first waste heat boiler, the air intake vent of sack cleaner and The air outlet connection of the first waste heat boiler, blower fan accesses the air outlet of sack cleaner, and the outlet of conveying worm carries with second The entrance connection of the machine of liter, the outlet of the second elevator is connected with the entrance of kiln ash feed bin, and kiln ash feed bin passes through the second elevator, spiral shell Rotation conveyer is connected with the bottom of the first waste heat boiler, the first cyclone dust extractor, sack cleaner respectively.
9. the process system for cement kiln synergic processing hazardous waste according to claim 2;It is characterized in that: waste heat Utilize system include for generate electricity the second waste heat boiler, the second cyclone dust extractor and air-introduced machine, the second cyclone dust extractor setting At the air intake vent of the second waste heat boiler, air-introduced machine is arranged on the air outlet of the second waste heat boiler.
10. the process system for cement kiln synergic processing hazardous waste according to claim 1;It is characterized in that: water Stall system includes cement kiln, dore furnace and desulfurizing tower/chimney, and cement kiln is connected with dore furnace;The tertiary-air pipe of cement kiln with Dangerous waste incineration kiln system connects, and dangerous waste incineration kiln system is connected with dore furnace;The kiln tail smoke-box of cement kiln and bypass Leak informaton and residual neat recovering system connection, bypass and residual neat recovering system are connected with desulfurizing tower/chimney.
CN201620865742.5U 2016-08-10 2016-08-10 A process systems that is used for cement kiln to deal with in coordination hazardous waste Active CN205897157U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201620865742.5U CN205897157U (en) 2016-08-10 2016-08-10 A process systems that is used for cement kiln to deal with in coordination hazardous waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201620865742.5U CN205897157U (en) 2016-08-10 2016-08-10 A process systems that is used for cement kiln to deal with in coordination hazardous waste

Publications (1)

Publication Number Publication Date
CN205897157U true CN205897157U (en) 2017-01-18

Family

ID=57781734

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201620865742.5U Active CN205897157U (en) 2016-08-10 2016-08-10 A process systems that is used for cement kiln to deal with in coordination hazardous waste

Country Status (1)

Country Link
CN (1) CN205897157U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106122980A (en) * 2016-08-10 2016-11-16 广州维港环保科技有限公司 A kind of process system for cement kiln synergic processing hazardous waste

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106122980A (en) * 2016-08-10 2016-11-16 广州维港环保科技有限公司 A kind of process system for cement kiln synergic processing hazardous waste
CN106122980B (en) * 2016-08-10 2019-07-09 广州维港环保科技有限公司 A kind of process system for cement kiln synergic processing hazardous waste

Similar Documents

Publication Publication Date Title
CN106122980B (en) A kind of process system for cement kiln synergic processing hazardous waste
CN102276130B (en) Sludge resource treatment apparatus and sludge treatment method using the same
CN105601075B (en) A kind of process and its device of pyrolyzing sludge carbonization treatment
CN102003713B (en) Device for combustible solid waste gasification and combustion
CN110734209A (en) Operation method of industrial solid waste and sludge rotary kiln co-processing integrated device
CN104033905B (en) System for combustible waste co-processing in cement kiln with bypass exhaust and waste heat power generation
CN104312600A (en) Sludge pyrolysis and gasification treatment process and sludge pyrolysis and gasification treatment system
CN107917427A (en) A kind of system and method for cement kiln synergic processing house refuse
CN203907628U (en) Sludge drying and burning system
CN205261566U (en) Solid organic waste resource is made up and is put
CN105385465B (en) A kind of refuse pyrolysis plant and method
CN104438296A (en) Dry-process rotary cement kiln cooperative household garbage treatment system and treatment method
CN105731754A (en) Treatment device and method for drying sludge through slag waste heat
CN101508902A (en) Biomass fuel cycle gasifying device and method thereof
CN201310895Y (en) Municipal domestic refuse drying pretreatment device
CN204276506U (en) A kind of dry method cement rotary kiln associated treatment house refuse system
CN205897157U (en) A process systems that is used for cement kiln to deal with in coordination hazardous waste
CN202107604U (en) Sludge resource processing apparatus
CN207514918U (en) A kind of rubbish cooperates with incinerating and treating device with semi-dry sludge
CN204138601U (en) A kind of pyrolyzing sludge gasification treatment system
CN100439255C (en) Process of extracting and utilizing solid matter of wheat straw pupl black liquid
CN107631304A (en) A kind of smoke circulating system suitable for cement kiln synergic processing house refuse
CN203768193U (en) Vitrified sludge disposal system
CN206661886U (en) The system for handling house refuse
CN206316118U (en) The system for handling house refuse

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant