CN110182838A - A kind of modified technique system and method for flue gas desulfurization ash - Google Patents

A kind of modified technique system and method for flue gas desulfurization ash Download PDF

Info

Publication number
CN110182838A
CN110182838A CN201910555301.3A CN201910555301A CN110182838A CN 110182838 A CN110182838 A CN 110182838A CN 201910555301 A CN201910555301 A CN 201910555301A CN 110182838 A CN110182838 A CN 110182838A
Authority
CN
China
Prior art keywords
solid
slurries
slurry
flue gas
gas desulfurization
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.)
Granted
Application number
CN201910555301.3A
Other languages
Chinese (zh)
Other versions
CN110182838B (en
Inventor
杨柳春
朱旻俊
尹诗诗
卢佳艳
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.)
Xiangtan University
Original Assignee
Xiangtan University
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 Xiangtan University filed Critical Xiangtan University
Priority to CN201910555301.3A priority Critical patent/CN110182838B/en
Publication of CN110182838A publication Critical patent/CN110182838A/en
Application granted granted Critical
Publication of CN110182838B publication Critical patent/CN110182838B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/464Sulfates of Ca from gases containing sulfur oxides
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B11/00Calcium sulfate cements
    • C04B11/02Methods and apparatus for dehydrating gypsum
    • C04B11/028Devices therefor characterised by the type of calcining devices used therefor or by the type of hemihydrate obtained
    • C04B11/032Devices therefor characterised by the type of calcining devices used therefor or by the type of hemihydrate obtained for the wet process, e.g. dehydrating in solution or under saturated vapour conditions, i.e. to obtain alpha-hemihydrate
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B11/00Calcium sulfate cements
    • C04B11/02Methods and apparatus for dehydrating gypsum
    • C04B11/028Devices therefor characterised by the type of calcining devices used therefor or by the type of hemihydrate obtained
    • C04B11/036Devices therefor characterised by the type of calcining devices used therefor or by the type of hemihydrate obtained for the dry process, e.g. dehydrating in a fluidised bed or in a rotary kiln, i.e. to obtain beta-hemihydrate
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B11/00Calcium sulfate cements
    • C04B11/26Calcium sulfate cements strating from chemical gypsum; starting from phosphogypsum or from waste, e.g. purification products of smoke
    • C04B11/262Calcium sulfate cements strating from chemical gypsum; starting from phosphogypsum or from waste, e.g. purification products of smoke waste gypsum other than phosphogypsum
    • C04B11/264Gypsum from the desulfurisation of flue gases
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Inorganic Chemistry (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention discloses a kind of modified technique system and methods of flue gas desulfurization ash.Modified technique system of the present invention includes ash cellar, acid tank, slurry tank, slurries pump, forces flow state reactivity device, slurry pool, solid-liquid separator, dehydration reactor, blower one, blower two.The method of the present invention is mainly on the basis of conventional aeration oxidation technology, the comprehensive gentle membranous wall of hard shell for abolishing desulfurization gray surface package using multiple enhancements is built, promote calcium sulfite and lime in Desulphurization all to expose and disperses, ensure to realize Efficient Conversion and stabilisation, while removing blending and covering property impurity to effectively improve product grade.It is different from conventional oxidation or method of modifying, Desulphurization is through the modified a variety of phase gypsum products for directly obtaining high-purity of system and method for the invention, it can be respectively used to downstream medium and high quality building material, self-leveling material, cementitious material and mould product etc., it is ensured that can be all by resource utilization.

Description

A kind of modified technique system and method for flue gas desulfurization ash
Technical field
The invention belongs to environmental protections and inorganic mineral material preparation technical field, and in particular to it is a kind of by calcium backbone method or The modified flue gas desulfurization for being converted to a variety of high purity gypsum powder products, realizing resource utilization of semi-dry process flue gas desulphurization by-product The modified technique system and method for ash.
Background technique
Sulfur dioxide in coal fired thermal power plant, steel, smelting and the flue gas of Industrial Stoves discharge is to cause acid rain, sulfuric acid cigarette The important component of mist and Brownish haze pollution, effective method of controlling is to implement in full flue gas desulfurization.In numerous flue gas desulfurization In technique, semidry method or dry flue gas desulphurization technique are with process is short, equipment is few, occupied area is small and excellent without technique waste water etc. Point is particularly suitable for applying in the flue-gas desulfurizing engineering of water-deficient area.Wherein, it as the calcium base semidry method of absorbent or is done using lime Method flue gas desulfurization technique occupies biggish market ratio because cost is relatively low.But the economical rationality of desulfurizing byproduct disposition becomes The a great problem that this kind of technique promotes and applies.
Calcium backbone method or the main component of semi-dry desulphurization ash are calcium sulfite, and contain the complete CaO of part unreacted Or Ca (OH)2, in addition there are the impurity such as calcium carbonate and flying dust.The partial size very little of Desulphurization, it is many de- generally mostly at 3~20 μm The Desulphurization of sulphur engineering output is based on the particle of 10 μm or less sizes.Have more experimental study and shows homogeneous sulphite Oxidation be easier to realize, but the Desulphurization of dry state deals with and wants much more difficult.Directly generally required with air dry oxidation Temperature is controlled at 400~700 DEG C, time-consuming 4~6h oxygenation efficiency can be only achieved 80% or more, and product is impure more nothing H 2 O calcium sulphate.Gas-liquid-solid three-phase wet oxidation is generally also required to be aerated for a long time, Desulphurization could be converted to calcium sulphate dihydrate Based on product, excess aeration energy consumption is quite big.There is research to attempt using strong oxidizers assisted oxidations such as hydrogen peroxide, ozone, or Person promotes oxidation process using additional catalyst, but cost is excessively high, using being restricted.Therefore, the modified work of conventional desulfurization ash Process is all that Desulphurization is converted to impurity more dihydrate gypsum or anhydrous gypsum, although being able to solve stability substantially Problem, but higher cost need to be paid, and only obtain low value mix products, it is big, economical that Desulphurization comprehensively utilizes difficulty It is ineffective.
Studies have shown that calcium-based desulfurization ash is the SO in pulverized limestone and flue gas2Undergo gas-liquid-solid phase reaction (semidry method) or Gas-particle two-phase reacts the product of (dry method): in a very short period of time, the SO in flue gas2It is brilliant that calcium sulfite is generated with lime reaction Body, while absorbent granules surface moisture evaporates quickly, forms fine and close product layer and is wrapped in fresh lime powder particle surface.It is this Product layer shell prevents further gas-solid desulphurization reaction, so that internal new fresh lime fails to expose and participate in react to be disappeared Consumption, thus residual quantity is larger.Meanwhile the superfine small Desulphurization of partial size is also mingled with other components of coal ash, and irregular shape is presented Looks and microstructure.Find that the fine grained outer surface of this dry state is also coated by one layer of air film, due to gas by further investigation Film has very strong compactness, and desulfurization ash particle is difficult to soak when with slurry, and dissolution reaction resistance increases, and reaction rate is limited System.So only being difficult to obtain efficient oxidation effectiveness by conventional aeration, impurity can not be effectively removed, improve product purity. We wrap up in air film and hard product shell double combination obstacle is started with from effectively abolishing outside particle, will using a variety of cooperative reinforcing measures Desulphurization highly effective reaction is stabilized simultaneously, removes the various impurity of product to improve purity, and further integrates dehydration and be modified Unit, to obtain a variety of gypsum products for having higher-value on a production line.
Summary of the invention
The first purpose of this invention be for energy consumption existing for conventional desulfurization ash modified technique method and it is at high cost and The problem of more added values of impurity in products are low, difficult utilization, provides a kind of modified technique system of flue gas desulfurization ash.
The first purpose of this invention is realized by the following technical solutions: the modified technique of flue gas desulfurization ash System, it includes ash cellar, acid tank, slurry tank, slurries pump, forces flow state reactivity device, slurry pool, solid-liquid separator, dehydration Device, blower one, blower two;The outlet of ash cellar and acid tank is connected to by pipeline with slurry tank, and blender is equipped in slurry tank;It forces Flow state reactivity device is located at the top of slurry pool, forces flow state reactivity device outlet at bottom by pipeline or is directly connected to slurry pool; The slurry tank outlet and slurries bottom of pond portion bypass outlet are pumped by slurries and the liquid phase of pipeline and the pressure flow state reactivity device Entrance connection;The bottom of slurry pool and slurry tank is connect with blower one by pipeline be passed through air aeration respectively;Slurry pool Outlet and the import of solid-liquid separator pass through piping connection, and the solid outlet of solid-liquid separator passes through conveyer belt or auger conveyor It is connected with the material inlet of dehydration reactor, the liquid-phase outlet of solid-liquid separator is connected to by pipeline with the slurry tank, Gu The top of liquid/gas separator is equipped with wash water entrance;The top of the dehydration reactor is equipped with exhaust outlet, exhaust outlet by blower two and Pipeline is connected to the air inlet for forcing flow state reactivity device, and dehydration reactor is connected with the pipeline for being passed through air or water vapour, Dehydration reactor bottom is equipped with solid matter outlet;Each pipeline is equipped with valve.
Specifically, the dehydration reactor uses the reactor with heating and temperature incubation function, quantity is 1~24, when When quantity is 2 or more, arranged using serial or parallel connection mode.
Specifically, the pressure flow state reactivity device includes necking segment i.e. venturi section and packing section, it which is provided with liquid phase and enter Mouthful and air inlet, several moveable spherical, spheroid shapes or cylindrical filler are built-in in packing section.
Specifically, the solid-liquid separator is using in vacuum band-type filter machine, vacuum drum or centrifugal separation equipment It is a kind of.
Second object of the present invention is to provide the flue gas desulfurization of the modified technique system based on above-mentioned flue gas desulfurization ash The modified technique method of ash, it includes the following steps:
(1) by ash cellar flue gas desulfurization ash and solid-liquid separator liquid-phase outlet recycle-water in slurry tank mixing preparation The slurries for being 12~50% at solid content, then with the pH value of sulfuric acid or hydrochloric acid adjusting slurries in acid tank to 3.5~7.5;
(2) 10~100min of air aeration is passed through into the slurries of slurry tank and slurry pool by blower one, passes through slurries Pump squeezes into the slurries in slurry tank and forces flow state reactivity device, and the air-flow for sending slurries with blower two comes into full contact with, and then one And enter slurry pool;
(3) it pumps to squeeze into the fraction slurries reflux in slurry pool by slurries and forces flow state reactivity device, and will be in slurry pool The dross of slurry surface is removed, and the slurries in slurry pool are then transferred to solid-liquid separator filtering and are washed simultaneously;
(4) filtrate in solid-liquid separator and wash water pass through its liquid-phase outlet and pipeline returns to slurry tank for deploying slurries With the solid isolated then is transferred in dehydration reactor;
(5) it is passed through air or water vapour into dehydration reactor and controls temperature and is carried out dehydrating at 60~300 DEG C, controls Solid material processed stops 2min~300min in dehydration reactor, is vented by blower two;
(6) after dehydration reactor cooling, solid material therein is drawn off to get steady to quality by its solid matter outlet Fixed high purity gypsum powder.
Specifically, the slurry tank and slurry pool aeration process, total aeration intensity is 1~30L/m2S controls gas The diameter of bubble is 0.1 μm~10mm.
Specifically, by forcing the gas velocity control of flow state reactivity device necking segment to control in 30~120m/s, liquid-gas ratio 10 ~300L/m3In the range of.Under the various effects such as the impact, shearing, suddenly changing pressure intensity of high-speed flow, desulfurization gray surface air film and Desulfurization product shell is destroyed, and the materials inside exposed is wetted, along with the suspension flow of built-in filler and desulfurization ash particle State is formed by strong turbulence, phase mutual friction and collision, so that Desulphurization causes gas-liquid-solid three by further grinding distribution Phase close contact, to efficiently carry out mass transfer and heat transfer.
Specifically, specific control method and condition are as follows when dehydration reactor operation:
When to produce the gypsum product of two water phases: being passed through air and control reactor temperature in 60~120 DEG C, solid phase Residence time of material is in 2min~60min range;When to produce the i.e. building gypsum product of β-gypsum containing half of crystallization water: logical Enter air and controls reactor temperature in 121~250 DEG C, solid-phase material residence time in 5min~120min range;When wanting Produce α-gypsum i.e. high strength gypsum product when: chemical additives commonly used in the art are added into solid-phase material, and are passed through saturation Water vapour generates saturated vapor from the moisture brought by heated material, at the same control reactor temperature 124~ 250 DEG C, the solid-phase material residence time is in 20min~300min range;When anhydrous gypsum product to be produced: being passed through air and control Temperature processed is in 251~400 DEG C, solid-phase material residence time in 30min~150min range.
Desulphurization modified technique method of the invention is comprehensive to be arranged using multiple reinforcing on the basis of conventional aeration oxidation technology The gentle membranous wall base of hard shell for abolishing desulfurization gray surface package is applied, calcium sulfite and lime all exposures in Desulphurization are promoted And disperse, it is ensured that realize Efficient Conversion and stabilisation, while removing blending and covering property impurity to effectively improve product grade. It is different from conventional oxidation or method of modifying, Desulphurization is through the modified high-purity that directly obtains of system and method for the invention A variety of phase gypsum products can be respectively used to downstream medium and high quality building material, self-leveling material, cementitious material and mould product Deng, it is ensured that it can be all by resource utilization.In addition, present invention process system can also be used for wet desulfurization system calcium base by-product The modification of (e.g., impure more desulfurization slag).Entire modified technique compact efficient, regulation is flexible, energy conservation and environmental protection, market Demand adaptability is very strong.
Protrusion effect performance of the invention is as follows:
(1) Desulphurization modified technique facility compact is efficient, process water whole circulating and recovering, modifying process energy conservation and environmental protection.
(2) integrate and mix entirely using gas-liquid-solid three-phase aeration, high-intensitive strength shearing broken shell, multimedium fluidization grinding point Dissipate and the multiple enhancements such as wet type thermal oxide ensure that Desulphurization is sufficiently converted into stable product, at the same effectively remove include it is miscellaneous Matter effectively improves mineral grade, gypsum raw material of the Desulphurization through the modified available high-purity of the method for the present invention.
(3) two water of output, Ban Shui can be flexibly controlled on a modified technique production line and without the gypsum powder body of water phase, i.e., Realize the gypsum product all standing of a variety of phases, therefore, product attribute and added value are capable of the variation of the flexible adaptation market demand, Ensure that Desulphurization or desulfurization slag can be all by resource utilizations.
Detailed description of the invention
Fig. 1 is the flowage structure schematic diagram of the modified technique system of flue gas desulfurization ash of the present invention.
Fig. 2 is the structural schematic diagram that flow state reactivity device is forced in Fig. 1.
Specific embodiment
The invention will be further described with reference to the accompanying drawings and examples.
Embodiment 1:
Referring to Fig. 1, the modified technique system of the flue gas desulfurization ash of the present embodiment, including ash cellar 1, acid tank 2, slurry tank 3, slurry Liquid pump 4 forces flow state reactivity device 5, slurry pool 6, solid-liquid separator 7, dehydration reactor 8, blower 1, blower 2 10.From Fig. 1 In as it can be seen that the outlet of ash cellar 1 and acid tank 2 be connected to by pipeline with slurry tank 3, slurry tank 3 is interior equipped with blender 11;Wherein, grey Desulphurization is transported to slurry tank 3 by pipeline by storehouse 1, and acid tank 2 is connected with slurry tank 3 by liquid line and passes through metering pump Acid solution is quantitatively adding slurry tank 3 by (being not drawn into figure).Force flow state reactivity device 5 be located on slurry pool 6, and with slurry pool 6 It is connected;Slurries pump 4 passes through liquid phase entrance and slurries of the pipeline respectively with the outlet of slurry tank 3, pressure flow state reactivity device 5 The bypass outlet in pond 6 is connected.The outlet of blower 1 passes through the gas distribution pipe and aeration of pipeline and 6 bottom of slurry tank 3 and slurry pool Element (being not drawn into figure) is connected.The outlet of slurry pool 6 and the import of solid-liquid separator 7 are separated by solid-liquid separation by piping connection The solid outlet of device 7 is connected by conveyer belt or auger conveyor with the material inlet of dehydration reactor 8, solid-liquid separator 7 Liquid-phase outlet be connected to slurry tank 3 by pipeline, the liquid phase for isolating solid-liquid separator 7 by pipeline sends slurry back to after collecting Liquid bath 3;The top of solid-liquid separator is equipped with wash water entrance.The top of dehydration reactor 8 is equipped with exhaust outlet, and exhaust outlet passes through blower 2 10 and pipeline with force flow state reactivity device 5 air inlet be connected to, dehydration reactor 8 is connected with the pipe for being passed through air or vapor Road, 8 bottom of dehydration reactor are equipped with solid matter outlet.Each pipeline in above system is equipped with valve (being not drawn into figure), For controlling the opening and closing of each pipeline.Referring to fig. 2, force have a necking segment 501 on the gas passage of flow state reactivity device 5 It is connected in series with a packing section 502,15~40 moveable plastics ball fillers is disposed in packing section 502, force stream State reactor 5 is equipped with liquid phase entrance 503 and air inlet 504.It is in parallel and have temperature adjustment function configured with 2 in the present embodiment The dehydration reactor 8 of energy passes through alternate operation and realizes semi continuous production.
The flue gas desulfurization ash modified technique system, to improve its degree of automation, the settable measurement in periphery and monitoring system System, including slurry pH value and temperature, gas and slurry flow, the monitoring of dehydration reactor temperature and pressure and display instrument, with And corresponding feedback control component;Wherein, slurry tank 3 and slurry pool 6 can be equipped with pH value and monitoring temperature instrument and respective feedback Control mechanism, gas piping is equipped with gas velocity tolerance monitoring device and accordingly controls executing agency, and dehydration reactor can be furnished with temperature With pressure monitor instrument and corresponding control executing agency etc..Because the equipment component and technology are existing mature technology, according to this skill The technique requirement of art scheme, this field or those skilled in the relevant arts can design and implementation, this will not be detailed here.
Here is that the engineering of the flue gas desulfurization ash modified technique method based on above-mentioned flue gas desulfurization ash modified technique system is real Example.
The semi-dry desulphurization ash of certain firms output is analyzed its main component calcium sulfite content 31%, calcium sulphate content 24%, calcium hydroxide content 26%, calcium carbonate 15%, other impurities 4% or so.
Method when implementing modified to Desulphurization using above-mentioned flue gas desulfurization ash modified technique system is as follows: to slurry tank 3 What the slave solid-liquid separator 7 of 1/2 volume of middle injection returned cross drainage, and by grey (about 1/10 slurry tank of flue gas desulfurization in ash cellar 1 Volume) injection slurry tank 3, it is stirred the suspension slurry for being deployed into quality solid holdup 30% or so, then by the sulfuric acid in acid tank 2 Solution is uniformly injected into above-mentioned suspension slurry, and controls slurry pH value to 4.0~5.0.Then blower 1 is opened, to slurry tank 3 Air is passed through in slurries, aeration intensity is in 2L/m in adjusting slurry tank2S or so simultaneously continues to be aerated 30min.Open slurries pump 4 Slurries in slurry tank 3 are squeezed into and force flow state reactivity device 5, while opening blower 2 10, send slurries and blower 2 10 Air-flow comes into full contact with latter and enters slurry pool 6, and gas empties (slurry pool is open) from slurry pool 6.Periodically by slurry pool 6 In fraction slurries squeeze into again and force flow state reactivity device 5, while air is passed through into slurry pool 6 by blower 1, adjusts slurry Aeration intensity is in 15L/m in liquid pool2S, aeration time 60min or so, and the dross of slurry surface in pond is disposed.Then Slurries are delivered to (using the vacuum belt filter) filtering of solid-liquid separator 7 and while being washed.Wherein, filtrate and wash water Slurry tank 3 is returned after collection to be then transferred in dehydration reactor 8 and be further processed for deploying slurries, the solid material isolated. It is passed through 200 DEG C or so of air into dehydration reactor 8 to be handled, constant temperature simultaneously controls solid material in dehydration reactor 8 5~10min is stopped, then by blower 2 10 and its pipeline connecting with dehydration reactor 8 exhaust, be vented body, which introduces, to be forced Flow state reactivity device 5.Solid material is drawn off after being cooled to 60 DEG C to get the building gypsum of 90% or more purity is arrived, can directly gone out It is sold after selling or being further processed into the gypsum powder body product of other specifications.Two dehydration reactors 8 feed and discharge in turn, are Fugitive dust is avoided, dust-precipitator can be matched in discharge port.
Embodiment 2:
The Desulphurization property of the present embodiment with embodiment 1, the flue gas desulfurization ash modified technique system of use with embodiment 1, Difference is operating method and modified product property when implementing modified to Desulphurization using the system.
Method when implementing modified to Desulphurization using above-mentioned flue gas desulfurization ash modified technique system is as follows: to slurry tank 3 What the slave solid-liquid separator 7 of 1/2 volume of middle injection returned cross drainage, and by grey (about 1/10 slurry tank of flue gas desulfurization in ash cellar 1 Volume) injection slurry tank 3, it is stirred the suspension slurry for being deployed into quality solid holdup 30% or so, then by the sulfuric acid in acid tank 2 Solution is uniformly injected into above-mentioned suspension slurry, and controls slurry pH value to 4.0~5.0.Then blower 1 is opened, to slurry tank 3 Air is passed through in slurries, aeration intensity is in 5L/m in regulating tank2S or so simultaneously continues to be aerated 30min.Slurries pump is opened slurries Slurries in slot 3, which are squeezed into, forces flow state reactivity device 5, while opening blower 2 10, and the air-flow for sending slurries with blower 2 10 fills Tap enters slurry pool 6 together after touch, and gas is emptied from slurry pool 6.Periodically the fraction slurries in slurry pool 6 are squeezed by force again Flow state reactivity device 5 processed, while being passed through air into slurry pool 6 by blower 1 adjusts in the pond aeration intensity in 20L/m2· S, aeration time 60min or so, and the dross of slurry surface in pond is disposed.Then slurries are delivered to solid-liquid separator 7 (using vacuum belt filter) filtering is simultaneously washed simultaneously.Wherein, filtrate and wash water return to slurry tank 3 for allotment after collecting Slurries are used, and the solid material isolated is mixed into the crystal control agent (sodium tartrate or malic acid) of solid gross mass 0.3% or so After be transferred in dehydration reactor 8 and be further processed.It is passed through 180 DEG C or so of water vapour into dehydration reactor 8 to be handled, controls Solid material processed stops 150min isothermal reaction in dehydration reactor 8, then by blower 2 10 and its with dehydration reactor 8 The pipeline of connection is vented, and be vented body, which introduces, forces flow state reactivity device 5.Solid material is drawn off after being cooled to 60 DEG C to get arriving α-gypsum of 90% or more purity.Two 8 alternation charging reactions of dehydration reactor and discharging can be in discharge ports to avoid fugitive dust Configure dust-precipitator.It can sell or be sold after being further processed into the high strength gypsum powder bodies of other specifications.
Embodiment 3:
The semi-dry desulphurization ash of certain firms output is analyzed its main component calcium sulfite content 26%, calcium sulphate content 28%, calcium hydroxide content 21%, calcium carbonate content 18%, other impurities 7% or so.Its modified technique system flow and composition Substantially with embodiment 1, difference is: the bypass outlet of slurry pool 6 by a newly-increased pump and pipeline and is forced to flow in system The liquid phase entrance 503 of state reactor 5 is connected, and the dehydration reactor in system 8 are furnished with 1.Using the system to de- Method when sulphur ash implements modified is as follows: the drainage of crossing of the return of slave solid-liquid separator 7 of 1/2 volume is injected into slurry tank 3, and Slurry tank 3 is injected into flue gas desulfurization grey (about 1/8 slurry tank volume) in ash cellar 1, is stirred and is deployed into quality solid holdup 35% or so suspension slurry, then the hydrochloric acid solution in acid tank 2 is uniformly injected into above-mentioned suspension slurry, and control slurry pH value extremely 5.5~6.5.Then blower 1 is opened, air is passed through into the slurries of slurry tank 3, aeration intensity is in 10L/m in regulating tank2· S or so simultaneously continues to be aerated 20min.It opens slurries pump and the slurries in slurry tank 3 is squeezed into pressure flow state reactivity device 5, open simultaneously Blower 2 10, makes slurries and air-flow that blower 2 10 is sent comes into full contact with latter and enters slurry pool 6, and gas is from 6 row of slurry pool It is empty.The fraction slurries in slurry pool 6 are squeezed into again every half an hour and force flow state reactivity device 5, while passing through blower 1 to slurry It is passed through air in liquid pool 6, adjusts in the pond aeration intensity in 12L/m2S, aeration 30min or so, and by slurry surface in pond Dross dispose.Then slurries are delivered to (using the vacuum belt filter) filtering of solid-liquid separator 7 and while carry out water It washes.Wherein, filtrate and wash water return to slurry tank 3 for deploying slurries after collecting, and it is anti-that the solid material isolated then is transferred to dehydration It answers and is further processed in device 8.It is passed through 60~80 DEG C of air into dehydration reactor 8 to be carried out dehydrating, controls solid material 60min or so is stopped in dehydration reactor 8, and passes through blower 2 10 and its pipeline connecting with dehydration reactor 8 exhaust, institute It is vented body and introduces pressure flow state reactivity device 5.Solid material is drawn off to get left to purity 95% to slightly cool down after the completion of dehydration Right dihydrate gypsum powder, can sell as downstream plastering raw material, or be further processed into other land plaster systems It is sold after product.
The above is only several examples in embodiment of the present invention, it can not be used to limit claim protection of the invention Range.Those skilled in the art of the present technique, can be in operating procedure and reaction item after understanding innovation and principle of the invention Make several modifications in terms of the combining form of part, or increase some links well known in the art, these modifications and Modification also should be regarded as without departing from protection scope of the present invention.

Claims (8)

1. a kind of modified technique system of flue gas desulfurization ash, it is characterised in that: it include ash cellar, acid tank, slurry tank, slurries pump, Force flow state reactivity device, slurry pool, solid-liquid separator, dehydration reactor, blower one, blower two;The outlet of ash cellar and acid tank is logical It crosses pipeline to be connected to slurry tank, blender is equipped in slurry tank;It forces flow state reactivity device to be located at the top of slurry pool, forces fluidised form Reactor bottom outlet is by pipeline or is directly connected to slurry pool;The slurry tank outlet and slurries bottom of pond portion bypass outlet are logical Slurries pump and pipeline is crossed to be connected to the liquid phase entrance for forcing flow state reactivity device;The bottom of slurry pool and slurry tank passes through respectively Pipeline connect with blower one and is passed through air aeration;The outlet of slurry pool and the import of solid-liquid separator pass through piping connection, Gu The solid outlet of liquid/gas separator is connected by conveyer belt or auger conveyor with the material inlet of dehydration reactor, is separated by solid-liquid separation The liquid-phase outlet of device is connected to by pipeline with the slurry tank, and the top of solid-liquid separator is equipped with wash water entrance;The dehydration is anti- The top of device is answered to be equipped with exhaust outlet, exhaust outlet is connected to by blower two and pipeline with the air inlet for forcing flow state reactivity device, Dehydration reactor is connected with the pipeline for being passed through air or water vapour, and dehydration reactor bottom is equipped with solid matter outlet;It is described each Pipeline is equipped with valve.
2. the modified technique system of flue gas desulfurization ash according to claim 1, it is characterised in that: the dehydration reactor uses Reactor with heating and temperature incubation function, quantity are 1~24, when quantity is 2 or more, using serial or parallel connection mode Arrangement.
3. the modified technique system of flue gas desulfurization ash according to claim 1, it is characterised in that: the pressure flow state reactivity device Including necking segment, that is, venturi section and packing section, liquid phase entrance and air inlet which is provided with, being built-in with several in packing section can Mobile spherical shape, spheroid shape or cylindrical filler.
4. the modified technique system of flue gas desulfurization ash according to claim 1, it is characterised in that: the solid-liquid separator is adopted With one of vacuum band-type filter machine, vacuum drum or centrifugal separation equipment.
5. a kind of modified technique side of the flue gas desulfurization ash of the modified technique system based on the ash of flue gas desulfurization described in claim 1 Method, it is characterised in that include the following steps:
(1) by ash cellar flue gas desulfurization ash and solid-liquid separator liquid-phase outlet recycle-water in slurry tank mixing preparation Cheng Gu The slurries that content is 12~50%, then with the pH value of sulfuric acid or hydrochloric acid adjusting slurries in acid tank to 3.5~7.5;
(2) it is passed through 10~100min of air aeration by slurries of the blower one into slurry tank and slurry pool, pumps handle by slurries Slurries in slurry tank, which are squeezed into, forces flow state reactivity device, and the air-flow for sending slurries with blower two comes into full contact with, then one goes forward side by side Enter slurry pool;
(3) it pumps to squeeze into the fraction slurries reflux in slurry pool by slurries and forces flow state reactivity device, and by slurries in slurry pool The dross on surface is removed, and the slurries in slurry pool are then transferred to solid-liquid separator filtering and are washed simultaneously;
(4) filtrate in solid-liquid separator and wash water pass through its liquid-phase outlet and pipeline returns to slurry tank for deploying slurries, divide The solid separated out is then transferred in dehydration reactor;
(5) it is passed through air or water vapour into dehydration reactor and controls temperature and is carried out dehydrating at 60~300 DEG C, control is solid Body material stops 2min~300min in dehydration reactor, is vented by blower two;
(6) after dehydration reactor cooling, solid material therein is drawn off to get stable to quality by its solid matter outlet High purity gypsum powder.
6. the modified technique method of the flue gas desulfurization ash of the modified technique system of flue gas desulfurization ash according to claim 5, Be characterized in that: the slurry tank and slurry pool aeration process, total aeration intensity are 1~30L/m2S controls the straight of bubble Diameter is 0.1 μm~10mm.
7. the modified technique method of the flue gas desulfurization ash of the modified technique system of flue gas desulfurization ash according to claim 5, It is characterized by and the gas velocity control of flow state reactivity device necking segment is forced to control in 30~120m/s, liquid-gas ratio in 10~300L/ m3In the range of.
8. the modified technique method of the flue gas desulfurization ash of the modified technique system of flue gas desulfurization ash according to claim 5, Be characterized in that: specific control method and condition are as follows when dehydration reactor operation:
When to produce the gypsum product of two water phases: being passed through air and control reactor temperature in 60~120 DEG C, solid-phase material Residence time is in 2min~60min range;When to produce the i.e. building gypsum product of β-gypsum containing half of crystallization water: being passed through sky Gas simultaneously controls reactor temperature in 121~250 DEG C, solid-phase material residence time in 5min~120min range;When producing When α-gypsum, that is, high strength gypsum product: chemical additives commonly used in the art being added into solid-phase material, and are passed through saturated water steaming Vapour generates saturated vapor from the moisture brought by heated material, while controlling reactor temperature 124~250 DEG C, the solid-phase material residence time is in 20min~300min range;When anhydrous gypsum product to be produced: being passed through air and control Temperature is in 251~400 DEG C, solid-phase material residence time in 30min~150min range.
CN201910555301.3A 2019-06-25 2019-06-25 Modification process system and method for flue gas desulfurization ash Active CN110182838B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910555301.3A CN110182838B (en) 2019-06-25 2019-06-25 Modification process system and method for flue gas desulfurization ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910555301.3A CN110182838B (en) 2019-06-25 2019-06-25 Modification process system and method for flue gas desulfurization ash

Publications (2)

Publication Number Publication Date
CN110182838A true CN110182838A (en) 2019-08-30
CN110182838B CN110182838B (en) 2023-10-17

Family

ID=67723263

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910555301.3A Active CN110182838B (en) 2019-06-25 2019-06-25 Modification process system and method for flue gas desulfurization ash

Country Status (1)

Country Link
CN (1) CN110182838B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111747438A (en) * 2020-05-25 2020-10-09 沈阳环境科学研究院 pH regulation and control multistep stabilization modification method for dry/semi-dry desulfurized fly ash

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1112454A (en) * 1994-04-28 1995-11-29 德拉沃石灰公司 Magnesium-enhanced sulfur dioxide scrubbing with gypsum formation
CN101053764A (en) * 2007-03-07 2007-10-17 沙晓农 Twin tower circulating fluidized bed fume desulfurizing method and device
CN201132104Y (en) * 2007-10-31 2008-10-15 浙江天蓝脱硫除尘有限公司 Desulfurizing device via method for oxidizing lime/carbide mud residue -gypsum out of the tower
CN101343077A (en) * 2008-07-21 2009-01-14 广东南方碱业股份有限公司 Method for preparing gypsum by removing boiler flue gas sulphur dioxide with white slime from ammonia alkali factory
CN104959018A (en) * 2015-06-25 2015-10-07 浙江天蓝环保技术股份有限公司 Device and method for redesulfuration with desulfurization ash
CN210103477U (en) * 2019-06-25 2020-02-21 湘潭大学 Modification process system of flue gas desulfurization ash

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1112454A (en) * 1994-04-28 1995-11-29 德拉沃石灰公司 Magnesium-enhanced sulfur dioxide scrubbing with gypsum formation
CN101053764A (en) * 2007-03-07 2007-10-17 沙晓农 Twin tower circulating fluidized bed fume desulfurizing method and device
CN201132104Y (en) * 2007-10-31 2008-10-15 浙江天蓝脱硫除尘有限公司 Desulfurizing device via method for oxidizing lime/carbide mud residue -gypsum out of the tower
CN101343077A (en) * 2008-07-21 2009-01-14 广东南方碱业股份有限公司 Method for preparing gypsum by removing boiler flue gas sulphur dioxide with white slime from ammonia alkali factory
CN104959018A (en) * 2015-06-25 2015-10-07 浙江天蓝环保技术股份有限公司 Device and method for redesulfuration with desulfurization ash
CN210103477U (en) * 2019-06-25 2020-02-21 湘潭大学 Modification process system of flue gas desulfurization ash

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111747438A (en) * 2020-05-25 2020-10-09 沈阳环境科学研究院 pH regulation and control multistep stabilization modification method for dry/semi-dry desulfurized fly ash
CN111747438B (en) * 2020-05-25 2022-12-06 沈阳环境科学研究院 pH regulation and control multistep stabilization modification method for dry/semi-dry desulfurized fly ash

Also Published As

Publication number Publication date
CN110182838B (en) 2023-10-17

Similar Documents

Publication Publication Date Title
CN104555946B (en) Method for jointly producing sulphuric acid and cement clinker by using sulphur gas to reduce gypsum
CN101797466A (en) Wet flue gas desulphurizing method utilizing carbide slag slurry and device thereof
CN104692689B (en) The method and its device of the modified oxidized calcium swelling agent of coproduction after a kind of flue gas dry desulfurizing
CN203469801U (en) Desulfurized ash-limestone mixing and slurrying device
CN110813046A (en) Double-circulation desulfurization device and desulfurization process
CN103861446B (en) Flue gas CO2With ardealite serous coat three-phase fluidization mineralization methods
CN110182838A (en) A kind of modified technique system and method for flue gas desulfurization ash
CN110052153A (en) A kind of desulfurizing agent preparation unit based on cement clinker production line calcium circulation
CN103301735B (en) Flue gas desulphurization and dust removal agent for small and medium sized boilers
CN210103477U (en) Modification process system of flue gas desulfurization ash
CN212581531U (en) Intermittent dry/semi-dry desulphurization ash stabilization modification system
CN110004286A (en) Modification coke powder and method of modifying and system, iron ore sintering method based on sintering low nitrogen oxide burning
CN109824285A (en) Cement fume desulfurizing agent and its application
CN110052152A (en) One kind being based on cement clinker production line calcium circulation desulfurization system and sulfur removal technology
CN110052151A (en) One kind being based on cement clinker production line calcium circulation half dry desulphurization system system
CN207933281U (en) Lime slaking device
CN216106021U (en) Furnace-process phosphoric acid production system
CN211189573U (en) High-efficient digestive system suitable for semi-dry process desulfurization
CN212581532U (en) Continuous dry method/semi-dry method desulfurization ash stabilization treatment system
CN210528560U (en) System for processing nitrate-containing wastewater by reduction method
CN205328846U (en) Two sections backward flow formula mud lime stabilization mummification systems
CN208927936U (en) A kind of flue-gas dust-removing and desulfurization denitrification integrated device
CN102515601B (en) Method and apparatus for modifying pozzolanic activity of mineral material
CN100363091C (en) Preparation of integrated desulfurizing agent during the two-stage digestible and separating process and its system thereof
CN112403216A (en) Method and device for flue gas desulfurization by using reduced magnesium slag

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant