CN102671618B - Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application - Google Patents

Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application Download PDF

Info

Publication number
CN102671618B
CN102671618B CN201210133472.5A CN201210133472A CN102671618B CN 102671618 B CN102671618 B CN 102671618B CN 201210133472 A CN201210133472 A CN 201210133472A CN 102671618 B CN102671618 B CN 102671618B
Authority
CN
China
Prior art keywords
adsorbent
gas
microsphere
fluidized bed
nano cao
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
CN201210133472.5A
Other languages
Chinese (zh)
Other versions
CN102671618A (en
Inventor
吴素芳
史余耀
吴嵘
薛孝宠
王燕
王樟茂
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.)
Zhejiang University ZJU
Original Assignee
Zhejiang University ZJU
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 Zhejiang University ZJU filed Critical Zhejiang University ZJU
Priority to CN201210133472.5A priority Critical patent/CN102671618B/en
Publication of CN102671618A publication Critical patent/CN102671618A/en
Application granted granted Critical
Publication of CN102671618B publication Critical patent/CN102671618B/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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/40Capture or disposal of greenhouse gases of CO2

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a preparation method for a microspherical nano CaO-based CO2 adsorber for a circulating fluidized bed. The preparation method comprises the following steps: dispersing nano CaCO3 in water to obtain suspension; stirring and mixing the suspension, additives and aluminum sol uniformly; performing spray granulation to obtain microspherical granules with the grain size of 20-200 micrometers; and calcining to obtain the microspherical nano CaO-based CO2 adsorber. The invention also discloses the microspherical nano CaO-based CO2 adsorber prepared by the method, and a method for capturing CO2 by using the microspherical nano CaO-based CO2 adsorber. The method is simple and feasible; the prepared adsorber has high adsorption speed, high adsorption capacity, high adsorption property and high wear resistance, the continuous decarbonization-regeneration circulating process can be realized in a circulating fluidized bed system, the capacity and efficiency of treating CO2 are greatly improved and the cost of removing the CO2 is reduced.

Description

A kind of microsphere nano CaO base CO for recirculating fluidized bed 2preparation method, product and the application of adsorbent
Technical field
The present invention relates to material manufacture and environmental protection, chemical process carbon dioxide removal field, be specifically related to a kind of microsphere nano CaO base CO for recirculating fluidized bed 2preparation method, product and the application of adsorbent.
Background technology
CO 2the 280ppm of content in atmosphere before by the industrial revolution risen to present 400ppm left and right, and it is the main cause that causes global warming.CO 2the main source of discharge is the combustion process of fossil fuel, reduces at present CO 2the means of discharge capacity are the CO to producing after combustion of fossil fuel 2trap, store and utilize, thereby reaching the object of effective reduction of discharging.
The CO that commercialization is now comparatively ripe 2capture method is wet method trapping, the CO in using amine aqueous solution as absorption liquid absorption from flue gas 2but the method also has several obvious shortcomings, first, owing to will, to the absorption liquid processing of regenerating, having increased energy consumption, the energy that has reduced whole system utilizes gross efficiency; Secondly,, in order to reduce the pollution of impurity to absorption liquid in flue gas, need to remove to flue gas the pretreatment of sulphur and nitrogen oxide; In addition, also have the problems such as equipment corrosion.The more important thing is and adopt wet method trapping meeting to the contaminated waste water of environmental emission, cause more pollution.
In the last few years, a kind of new CO 2the trapping of trapping technique-dry method receives increasing concern, different from wet method trapping, and dry method trapping adopts solid absorbent to the CO in flue gas 2adsorb, cardinal principle is to utilize the active component in adsorbent to adsorb the CO in flue gas at adsorptive reactor 2formed hydrochlorate, reduces the CO in flue gas 2concentration, subsequently, adsorbent is transported in calcination reactor regenerates, and realizes recycling of adsorbent.It is cheap that dry method trapping technique has raw material, renewable, flexible design, eco-friendly advantage.
CO 2the recirculating fluidized bed system of dry method trapping process using has had certain research at present, circulating fluidized bed technique is widely used in the catalytic cracking (FCC of oil refining, fluid catalytic cracking) and fluidized bed combustion reactor (CFBC, circulating fluidized bed combustion).Therefore circulating fluid bed reactor is used for to CO 2in trapping, do not have technological difficulties, and compare under this individual system, the physical property of adsorbent is still the primary difficult problem solving in world wide as the stability of adsorption capacity as wear rate and chemical property.Because these property relationships are to the Cost Problems of dry method decarburization.
Natural limestone and dolomite etc. taking calcium oxide as active component is considered to have the dry method trapping adsorbent of large development potentiality, but has two larger defects: the easy decay of adsorption capacity and adsorbent are easy to wear.
The people such as Dennis (Lu et al., Fuel Process.Technol.2008,12 of 89,1386-1395) adopt the fluidized-bed reactor CO absorption of lime stone at pilot-scale 2, in practical operation, the temperature of absorber is controlled at 580-720 DEG C, and the temperature in regenerator is controlled at 850-950 DEG C, CO 2volume content is at 15-16%, and after 15 circulations, specific area has declined 31.9%, and after 25 circulations, adsorption efficiency has declined 26.8%, and material has worn and torn 62%.
The people such as Symonds (Symonds et al., Chem.Eng.Sci.2009,15of 64,3536-3543) adopt lime stone CO absorption on fluid bed 2, adsorption temp is 550 DEG C, atmosphere is 8%CO 2, 17%H 2the air of O; Regeneration temperature is 860 DEG C; After three circulations, more than 95% time of adsorption efficiency has declined 80%.
The people such as the Li Zhenshan of Tsing-Hua University (Fang et al., Ind.Eng.Chem.Res.2009,24of48,11140-11147) utilize dolomite as adsorbent CO absorption on two bubbling beds 2, adsorption temp is 600 DEG C, CO 213.4% air); Regeneration temperature is 900 DEG C, and in 250min, adsorbent has lost 11.5%, and the adsorbent average grain diameter of calcining compartment has declined 68%.
It is all the system of quick Bed that the people such as Alonso (Alonso et al., Int.J.Greech.Gas Control.2010,2of 4,167-173) have adopted absorber and regenerator.The operating temperature of absorber is 600-700 DEG C, with air and CO 2gaseous mixture is conveying gas, and the temperature of regenerator is 800-900 DEG C, and fluidized gas is air.CO 2adsorption efficiency all remain on more than 70%, but the CO in adsorbed gas is not described 2concentration, can infer its CO according to other scholars' result of study 2treating capacity should be in a lower level.
People (the Gonz á lez et al. such as Gonz á lez, Fuel 2010,10of89,2918-2924) adopt same device and operating condition, the wear rate of limestone particle of two kinds of different-grain diameters of research: after circulation 40-100 hour, the average grain diameter 38%-50% that declined.
The adsorption capacity of natural limestone adsorbent is low, the rate of adsorption is slow, therefore taking natural limestone adsorbent when recycle stock carrys out reactor design, adsorptive reactor generally adopts the smaller fluid bed form of the gas such as moving bed or bubbling bed agent to ensure CO 2removal effect, but increased Material Cost and the cost of energy of processing unit volume flue gas.And adopt fast fluidized bed as adsorptive reactor, although can increase gas agent ratio, because absorbent particles polishing machine is poor, in order to ensure essential CO 2trapping effect, need to ceaselessly supplement fresh adsorbent, needs more expense of raw materials, has caused CO 2the rising of processing cost, this is one of key that at present cannot industrial applications.The calcium oxide-based carbon dioxide for recirculating fluidized bed of report adsorbs the stability of the adsorption capacity that does not also solve adsorbent and problem easy to wear at present.
For CaO base CO 2adsorbent is decay and shortcoming easy to wear easily, and the inventor (Su F.Wu, Ind.Eng.Chem.Res, 2008,47,180-184) in early-stage Study adopts the presoma that nano-calcium carbonate is calcium oxide-based adsorbent, preparation nanometer CaO/Al 2o 3adsorbent, finds nanometer CaO/Al 2o 3adsorbent has CO 2the advantages such as adsorption rate is high, decomposition temperature is low, the rate of adsorption is fast.The inventor is to disclose respectively employing precipitation of silica and the coated CaTiO in surface in CN101306309A and the publication number Chinese patent that is CN101537339A at publication number 3method nano-calcium base adsorbent is carried out to modification, under TGA test, adsorption capacity and absorption stability are significantly improved, but both not yet propose the adsorbent of modification to make microsphere particle, and the intensity of adsorbent and abrasiveness far do not reach the requirement of fluid bed system.
In the Chinese patent that the inventor is CN101961638A at publication number, disclose one and prepared the calcium oxide-based CO of nanometer antiwear 2the method of adsorbent, by CaCO 3particle ultrasonic wave in water disperses, and adds aluminium colloidal sol, is stirred to uniform sizing material, obtains the microsphere particle that particle diameter is 20-250 μ m, then obtain spherical wear-resisting nano oxidized Ca-base adsorbent by calcining by mist projection granulating.Owing to having formed calcium aluminate in calcination process, the wearability of calcium oxide is improved, but this adsorbent does not solve the problem that adsorption capacity is low, adsorption capacity is less than 2mol/kg.
Tang Qi is in master thesis (Zhejiang University, 2011) in, mention in composite catalyst preparation and adopt aluminium carbonate ammonium, polyethylene glycol, softex kw and activated carbon as expanding agent, but in CaO group carbonic anhydride adsorption agent preparation process, do not use.Other are not reported for the research of circulating fluidized bed technique capturing carbon dioxide about nano oxidized calcium group carbonic anhydride adsorption agent.
Summary of the invention
The invention provides a kind of microsphere nano CaO base CO for recirculating fluidized bed 2the preparation method of adsorbent, simple, the adsorbent of preparation is wear-resistant, the rate of adsorption is fast, adsorption capacity is high.
A kind of microsphere nano CaO base CO for recirculating fluidized bed 2the preparation method of adsorbent, comprising: nanometer CaCO 3be scattered in and in water, form suspension, suspension, additive and aluminium colloidal sol are uniformly mixed to evenly, obtaining particle diameter through mist projection granulating is the microsphere particle of 20~200 microns, then obtains microsphere nano CaO base CO after calcining 2adsorbent.
Described additive is aluminium carbonate ammonium, polyethylene glycol or nano-sized carbon, adds additive to prepare to have the microsphere nano CaO base CO of certain pore size structure and specific area 2adsorbent, strengthens mass transfer, heat-transfer effect in adsorbent and carbon dioxide reaction process, improves wearability, adsorption capacity and stability.
Described aluminium colloidal sol is to be hydrolyzed by aluminium salt and alcoholic solution the industrial goods forming, and its composition is for containing Al 2o 3colloidal solution.Al in conventional aluminium colloidal sol 2o 3mass fraction be 5%~20%.
Described nanometer CaCO 3in Ca and the mol ratio of Al in aluminium colloidal sol be 0.1~50: 1, to improve microsphere nano CaO base CO 2the anti-wear performance of adsorbent.
Described additive and nanometer CaCO 3mass ratio be 0.005~0.2: 1, to strengthen microsphere nano CaO base CO 2the mass transfer of adsorbent, heat-transfer effect, improve adsorption capacity and stability.
Described calcining is at 750~1000 DEG C, to calcine 1~8h, nanometer CaCO after calcining 3resolve into nanometer CaO and make microsphere nano CaO base CO 2adsorbent.
The present invention also provides the microsphere nano CaO base CO that adopts above-mentioned preparation method to prepare 2adsorbent.
Further, the present invention also provides above-mentioned microsphere nano CaO base CO 2adsorbent is applied to and in recirculating fluidized bed, traps CO 2method, comprise the following steps:
(1) by microsphere nano CaO base CO 2adsorbent packs in circulating fluid bed reactor, contains CO to passing in reactor 2fluidized gas, carry out adsorption reaction;
(2) CO absorption in reactor 2after adsorbent and CO 2fluidized gas after being adsorbed enters cyclone separator and separates, and the solid after separation enters regenerator, the gas discharging after separation;
(3) regenerator bottoms passes into N 2, CO 2or the tail gas that regenerator produces is as loosening gas, carries out the regeneration of adsorbent.
Described fluidized gas is for containing CO 2flue gas; The gas speed of described fluidized gas in adsorptive reactor is 1~1000 times of adsorbent microballoon minimum fluidizing velocity; The described CO that contains 2flue gas in CO 2volumetric concentration be 8%~20%, in actual application, need and contain CO according to the space size of reactor 2the choose reasonable microsphere nano CaO base CO such as treating capacity of flue gas 2the consumption of adsorbent.
Different speed, the adsorption effects that can affect absorption of adsorption temp, are the disposal ability that improves carbon dioxide, need to select suitable adsorption temp, and the temperature of the adsorption reaction of described step (1) is 550~650 DEG C.
Described loosening gas is the tail gas that regenerator produces, and described tail gas is the N mixing with arbitrary proportion 2and CO 2mist; The gas speed of described loosening gas is 1~20 times of adsorbent microsphere particle minimum fluidizing velocity, with keep absorbent particles in reactor in fluidized state.
CO absorption 2after adsorbent need to carry out thermal decomposition regeneration again to carry out adsorption reaction, the temperature of the regeneration of described step (4) is 750~950 DEG C.
Principle of the present invention is:
Nanometer CaO base CO 2caO in adsorbent and CO 2reaction generates CaCO 3:
C aO (s)+CO 2→C aCO 3(s) (1)
The CaCO that reaction generates 3by heating disintegrating and regeneration, reaction equation is as follows:
C aC O3(s)→C aO (s)+CO 2 (2)
Adsorbent after the present invention's regeneration carries out adsorption-regeneration circulation according to step (1)~(4) again; CO in the gas obtaining after cyclonic separation more than 90% 2be removed CO 2concentration remains on below 1%, can directly be disposed to atmosphere; Microsphere nano CaO base CO 2caCO in adsorbent 3cO in the tail gas producing after regeneration 2concentration is more than 50%.
Compared with prior art, the invention has the advantages that:
The inventive method is simple, prepares particle diameter and be the microsphere nano CaO base CO of 20~200 microns 2adsorbent, its specific area can reach 10m 2more than/g, in absorbent particles, pore and large hole count are all increased, and average pore size is in 8~20 nanometers.
Microsphere nano CaO base CO of the present invention 2adsorbent has good polishing machine, according to ASTM D5757 standard (Standard test method for determination of attrition and abrasion of powder catalysts by air jets, ASTM, US) wear rate of absorbent particles of test is below 5%.Microsphere nano CaO base CO of the present invention 2adsorbent has good absorption property, in TGA test, after 50 adsorption-desorption circulations, more than its adsorption capacity still remains on 3mol/kg adsorbent.
Microsphere nano CaO base CO of the present invention 2adsorbent, has good mass transfer, heat transfer property, is applied in recirculating fluidized bed decarbonization process, and compared with natural calcium oxide-based adsorbent, required regeneration temperature and adsorption reaction temperature have reduced by 50~100 DEG C, have reduced and have removed CO 2cost of energy.
Microsphere nano CaO base C of the present invention o2 adsorbents, than natural base adsorbent, have larger adsorption capacity and adsorption rate faster, have ensured that adsorbent is at recirculating fluidized bed CO 2in trapping technique, can adopt fast fluidized bed decarburization, reach the object that improves reactor for treatment amount; There is better polishing machine, greatly reduce and remove CO 2material Cost.
Microsphere nano CaO base CO of the present invention 2absorbent preparation technique is simple, is applied to and in recirculating fluidized bed, traps CO 2method, can continous-stable operation, mass transfer, heat transfer efficiency are high.
Brief description of the drawings
Fig. 1 is microsphere nano CaO base CO of the present invention 2the preparation method's of adsorbent flow chart.
Fig. 2 is the microsphere nano CaO base CO of the different specific areas prepared of comparative example 1 of the present invention and embodiment 1 2the adsorpting rate curve figure of adsorbent nsorb-1 and sorb-2.
Fig. 3 is the microsphere nano CaO base CO of the different specific areas prepared of comparative example 1 of the present invention and embodiment 1 2the circulation absorption Capacity Plan of adsorbent nsorb-1 and sorb-2.
Fig. 4 is microsphere nano CaO base CO prepared by the embodiment of the present invention 4 2the CO of adsorbent sorb-5 the 40 circulation absorption in fixed bed test 2adsorption efficiency and outlet CO 2concentration map, actual conditions is as follows: adsorbent mass 5g, CO 2concentration is 20%, 600 DEG C of adsorption temps, 800 DEG C of regeneration temperatures.
Fig. 5 is microsphere nano CaO base CO of the present invention 2capture by Sorbents CO 2the schematic diagram of method.
Detailed description of the invention
Describe the present invention in detail below in conjunction with embodiment, but the present invention is not limited to this.
Comparative example 1
Nanometer CaCO 310g is dispersed in 80ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 10.2g mass fraction is 10% aluminium colloidal sol, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 5 microns.Absorbent particles is calcined to 1h at 800 DEG C, obtain microsphere nano CaO base CO 2adsorbent, nsorb-1.
Embodiment 1 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 310g is dispersed in 50ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 51g mass fraction is 20% aluminium colloidal sol and 1.5g aluminium carbonate ammonium, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 20 microns.Absorbent particles is calcined to 1h at 880 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-2.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 4.0%.
Embodiment 2 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 320g is dispersed in 160ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 8.16g mass fraction is 5% aluminium colloidal sol and 4g polyethylene glycol, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 200 microns.Absorbent particles is calcined to 4h at 1000 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-3.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 3.3%.
Embodiment 3 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 320g is dispersed in 100ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 20.4g mass fraction is 10% aluminium colloidal sol and 0.1g Macrogol 2000, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 60 microns.Absorbent particles is calcined to 2h at 850 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-4.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 5.0%.
Embodiment 4 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 315g is dispersed in 150ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 38.25g mass fraction is 5% aluminium colloidal sol and 3g aluminium carbonate ammonium, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 80 microns.Absorbent particles is calcined to 2h at 900 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-5.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 4.8%.
Embodiment 5 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 310g is dispersed in 60ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 15.7g mass fraction is that 5% aluminium colloidal sol and 1.5g particle diameter are the powdered carbon of 100 nanometers, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 80 microns.Absorbent particles is calcined to 2h at 850 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-6.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 3.7%.
Embodiment 6 microsphere nano CaO base CO 2the preparation of adsorbent
Nanometer CaCO 310g is dispersed in 70ml distilled water, forms finely dispersed suspension, to nanometer CaCO 3in suspension, adding 8.5g mass fraction is the powdered carbon that 20% aluminium colloidal sol and 2g particle diameter are 100, fully mixes, and forms uniform slurry.Slurry is through mist projection granulating, obtains grain diameter and be the solid sorbent particles of 60 microns.Absorbent particles is calcined to 2h at 900 DEG C, obtain microsphere nano CaO base CO 2adsorbent, sorb-7.
Microsphere nano CaO base CO prepared by the present embodiment 2absorbent particles wear rate is 3.1%.
Application examples recirculating fluidized bed decarbonization process
Microsphere nano CaO base CO 2capture by Sorbents CO 2technique, as shown in Figure 5, fresh particles nanometer CaO base CO 2adsorbent, in conveying device enters the reactor of recirculating fluidized bed, meanwhile, passes into and contains CO to adsorptive reactor 2flue gas, CO 2after contacting with adsorbent microballoon, adsorbed rapidly, the gas-solid mixture that leaves adsorptive reactor enters cyclone separator and separates, gas after separation directly discharges atmosphere, adsorbent solids after separation is transported in regenerator, the tail gas of regenerator passes in regenerator as loosening gas, carry out adsorbent reactivation reaction, the adsorbent after regeneration enters adsorption-regeneration circulation next time.
Application examples 1
Adopt the CO in recirculating fluidized bed decarbonization process trapping flue gas 2, the microsphere nano CaO base CO that the adsorbent of use is prepared for the embodiment of the present invention 1 2adsorbent sorb-2, average grain diameter is 20 microns, adsorption reaction condition is: 800 DEG C of regeneration temperatures, loosening gas speed is 30 times of adsorbent microballoon minimum fluidizing velocity, the gas agent that enters adsorptive reactor is than being 0.083L/g, wherein CO 2concentration 15vol%, 600 DEG C of adsorption temps, CO in exit gas 2content is 0.3vol%, CO 2adsorption efficiency 98.3%.
Application examples 2
Adopt the CO in recirculating fluidized bed decarbonization process trapping flue gas 2, the microsphere nano CaO base CO that the adsorbent of use is prepared for the embodiment of the present invention 1 2adsorbent sorb-2, average grain diameter is 20 microns, adsorption reaction condition is: 780 DEG C of regeneration temperatures, loosening gas speed is 40 times of adsorbent microballoon minimum fluidizing velocity, the gas agent that enters adsorptive reactor is than being 0.08L/g, wherein CO 2concentration 15vol%, 550 DEG C of adsorption temps, CO in exit gas 2content 0.5vol%, CO 2adsorption efficiency 97.18%.
Application examples 3
Adopt the CO in recirculating fluidized bed decarbonization process trapping flue gas 2, the microsphere nano CaO base CO that the adsorbent of use is prepared for the embodiment of the present invention 2 2adsorbent sorb-3, average grain diameter is 200 microns, adsorption reaction condition: 800 DEG C of regeneration temperatures, loosening gas speed is 60 times of adsorbent microballoon minimum fluidizing velocity, the gas agent that enters adsorptive reactor is than being 0.05L/g, wherein CO 2concentration 20vol%, 550 DEG C of adsorption temps, CO in exit gas 2content 0, CO 2adsorption efficiency 100%.
Application examples 4
Adopt the CO in recirculating fluidized bed decarbonization process trapping flue gas 2, the microsphere nano CaO base CO that the adsorbent of use is prepared for the embodiment of the present invention 5 2adsorbent sorb-6, average grain diameter is 80 microns, adsorption reaction condition: 850 DEG C of regeneration temperatures, loosening gas speed is 40 times of adsorbent microballoon minimum fluidizing velocity, the gas agent that enters adsorptive reactor is than being 0.06L/g, wherein CO 2concentration 8vol%, 650 DEG C of adsorption temps, CO in exit gas 2content is at 0vol%, CO 2adsorption efficiency 100%.
Application examples 5
Adopt the CO in recirculating fluidized bed decarbonization process trapping flue gas 2, the microsphere nano CaO base CO that the adsorbent of use is prepared for the embodiment of the present invention 4 2adsorbent sorb-5, average grain diameter is 80 microns; Adsorption reaction condition: 750 DEG C of regeneration temperatures, loosening gas speed is 40 times of adsorbent microballoon minimum fluidizing velocity, the gas agent that enters adsorptive reactor is than being 0.075L/g, wherein CO 2concentration 20vol%, 600 DEG C of adsorption temps, the staying volume 2kg of adsorbent in riser, CO in exit gas 2content is at 1vol%, CO 2adsorption efficiency 90%.

Claims (4)

1. a microsphere nano CaO base CO 2adsorbent is applied to and in recirculating fluidized bed, traps CO 2method, it is characterized in that, comprising:
(1) by microsphere nano CaO base CO 2adsorbent packs in circulating fluid bed reactor, contains CO to passing in reactor 2fluidized gas, carry out adsorption reaction;
(2) CO absorption in reactor 2after adsorbent and CO 2fluidized gas after being adsorbed enters cyclone separator and separates, and the solid after separation enters regenerator, the gas discharging after separation;
(3) regenerator bottoms passes into N 2, CO 2or the tail gas that regenerator produces is as loosening gas, carries out the regeneration of adsorbent;
Described fluidized gas is for containing CO 2flue gas, the gas speed of described fluidized gas is 1~1000 times of adsorbent microballoon minimum fluidizing velocity, the described CO that contains 2flue gas in CO 2volumetric concentration be 8%~20%;
Described loosening gas is the tail gas that regenerator produces, and described tail gas is CO 2and N 2mist; The gas speed of described loosening gas is 1~20 times of adsorbent microsphere particle minimum fluidizing velocity;
Described microsphere nano CaO base CO 2the preparation method of adsorbent, comprising: nanometer CaCO 3be scattered in and in water, form suspension, suspension, additive and aluminium colloidal sol are uniformly mixed to evenly, obtaining particle diameter through mist projection granulating is the microsphere particle of 20~200 microns, then obtains microsphere nano CaO base CO after calcining 2adsorbent;
Described additive is aluminium carbonate ammonium, polyethylene glycol or nano-sized carbon;
Described nanometer CaCO 3in Ca and the mol ratio of Al in aluminium colloidal sol be 0.1~50:1, described additive and nanometer CaCO 3mass ratio be 0.005~0.2:1.
2. microsphere nano CaO base CO as claimed in claim 1 2adsorbent is applied to and in recirculating fluidized bed, traps CO 2method, it is characterized in that, described calcining for to calcine 1~8h at 750~1000 DEG C.
3. microsphere nano CaO base CO as claimed in claim 1 2adsorbent is applied to and in recirculating fluidized bed, traps CO 2method, it is characterized in that, the temperature of the adsorption reaction of step (1) is 550~650 DEG C.
4. microsphere nano CaO base CO as claimed in claim 1 2adsorbent is applied to and in recirculating fluidized bed, traps CO 2method, it is characterized in that, the temperature of the regeneration of step (3) is 750~950 DEG C.
CN201210133472.5A 2012-04-28 2012-04-28 Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application Active CN102671618B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210133472.5A CN102671618B (en) 2012-04-28 2012-04-28 Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210133472.5A CN102671618B (en) 2012-04-28 2012-04-28 Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application

Publications (2)

Publication Number Publication Date
CN102671618A CN102671618A (en) 2012-09-19
CN102671618B true CN102671618B (en) 2014-07-30

Family

ID=46804558

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210133472.5A Active CN102671618B (en) 2012-04-28 2012-04-28 Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application

Country Status (1)

Country Link
CN (1) CN102671618B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104190208A (en) * 2014-08-12 2014-12-10 清本环保工程(杭州)有限公司 Method for treating organic waste gas by using circulating fluidized bed
CN104289173B (en) * 2014-09-30 2016-11-23 浙江大学 A kind of lithium salts blends carbon dioxide absorber presoma and the application thereof of nano-calcium carbonate
CN106475041A (en) * 2016-11-25 2017-03-08 清华大学 A kind of Nano-meter SiO_22The synthetic method of/CaO adsorbent and application
CN114162825B (en) * 2020-09-11 2023-07-04 北京清创硅谷科技有限公司 Method and device for producing nano-coated material or nano-hollow material

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101961638B (en) * 2010-10-22 2012-09-19 浙江大学 Method for preparing wear-resistant nano calcium oxide-based carbon dioxide reaction adsorbent

Also Published As

Publication number Publication date
CN102671618A (en) 2012-09-19

Similar Documents

Publication Publication Date Title
Zhang et al. Removal of elemental mercury from simulated flue gas by ZSM-5 modified with Mn-Fe mixed oxides
Yang et al. Removal of elemental mercury from flue gas using wheat straw chars modified by Mn-Ce mixed oxides with ultrasonic-assisted impregnation
Shan et al. Preparation of microwave-activated magnetic bio-char adsorbent and study on removal of elemental mercury from flue gas
Heidari et al. CO2 capture and fluidity performance of CaO-based sorbents: Effect of Zr, Al and Ce additives in tri-, bi-and mono-metallic configurations
Liu et al. Recent developments in novel sorbents for flue gas clean up
AU2016208969B2 (en) Method for waste gas dedusting and dedusting agent
CN102674424B (en) Method for preparing nanometer calcium carbonate slurry by using waste gypsum as calcium sources, products and application
CN103998123B (en) The drikold absorbent containing amine or its compound being used in the capture method of dry carbon dioxide and manufacture method thereof
JP6194356B2 (en) Renewable sorbent for removing carbon dioxide
CN102671618B (en) Preparation method for microspherical nano CaO-based CO2 adsorber for circulating fluidized bed, product and application
Chen et al. Simultaneous removal of HCHO and elemental mercury from flue gas over Co-Ce oxides supported on activated coke impregnated by sulfuric acid
CN103240098B (en) Catalyst component and method for removing sulfur oxides and nitric oxides from smoke
JP2008540083A (en) Scavengers for removing acid gases from fluid streams
CA2939524A1 (en) Desulfurization apparatus and exhaust gas processing system using the same
CN107684811B (en) A kind of rotary cyclic carbon capturing device and method based on three reactions
Kotyczka-Moranska et al. Comparison of different methods for enhancing CO2capture by CaO-based sorbents. Review
Yu et al. Preparation, characterization of Ca/Al carbonate pellets with TiO2 binder and CO2 sorption at elevated-temperature conditions
CN105749863A (en) Compound desulfurizer and preparation method thereof
CN101298017A (en) Flue gas desulfurization and denitration technique
CN107282066A (en) A kind of SCR denitration and its methods for making and using same based on Natural Manganese iron ore
Lee et al. CO2 capture from flue gas using potassium-based dry regenerable sorbents
CN102210968A (en) Method for desulfurizing hydrogen sulfide-containing mixed gas
Conte et al. Sequential separation of cobalt and lithium by sorption: Sorbent set selection
Wu et al. SO2 resistance of CeO2-and Co3O4-supported activated carbon during removal of mercury from flue gas: A comparative study
Andinia et al. Mechanochemical processing of blast furnace slag for its reuse as adsorbent

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant