CN101015810A - Regeneration method and device of catalysis-adsorption agent for flue gas denitrification - Google Patents
Regeneration method and device of catalysis-adsorption agent for flue gas denitrification Download PDFInfo
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Abstract
The invention relates to a regenerating method of catalyst-absorber used to denitrify smoke, wherein the invention uses steam regenerating method to fill the magnesia-base catalyst-absorber treated with denitrify treatment into resistant furnace, increasing the temperature of resistant furnace to 200-500Deg. C, feeding in the steam at 100-200Deg. C, controlling the steam pressure to 0.05MPa-1MPa for 20-60min, controlling the flux of steam at 1000-2000h-1, and the internal pressure of the furnace at 0.05-0.5MPa, passing the steam through the catalyst layer in the furnace, adsorbing and discharging the tail gas via Na2CO3 solution. The resistant furnace is upright steam activate resistant furnace, whose case and cylinder are barrels, between which the annular space comprises a flameproof thermal insulated layer and a heating tube from outer to inner. The invention can keep high activity after regenerating catalyst-absorber, to hold the stability of denitrification.
Description
Technical field
The invention belongs to environmental technology field, relate to the improvement technology of coal-fired flue-gas, be specifically related to the regeneration activating technology of catalysis-adsorption agent for flue gas denitrification.
Background technology
Along with deepening continuously that the strategy of sustainable development is familiar with, Environmental Pollution and Control's problem has caused the great attention of countries in the world.Wherein the pollution of acid rain and the harm that causes thereof have become one of global environment problem of paying close attention to countries in the world.The main source of sour gas is the pernicious gas in enterprise's discharged gas fumes such as burning, thermal power generation, smelting iron and steel, non-ferrous metal metallurgy, cement and relevant chemical plant in the atmosphere: nitrogen oxide, oxysulfide, oxycarbide etc., moisture in they and the atmosphere, through photochemistry and non-photochemical, homogeneous phase and heterogeneous atmosphere chemically react, form the acid rain of PH＜5.6.
SO
2And NO
xBe that discharge capacity is maximum in the atmosphere pollution, two kinds of gases of harmfulness maximum also are the main matter that forms acid rain, and their dry deposition does great damage to ecology with falling, and influences health.China is to be the country of main energy sources with the coal, and it is about 70% that coal accounts in primary energy, and wherein utilizes by combustion system more than 84% (1,000,000,000 tons/year), contains SO and coal combustion produces
2(1000～4000ppm) and NO
x(300～800ppm) combustion gas is that industrial waste gas pollutes the main root of (acid rain harm).
Along with rapid development of national economy, China has become production of energy and consumption big country, and the discharge capacity of consequent sulfur dioxide and nitrogen oxide also increases year by year, ranks first in the world at present.Discharge capacity to national sulfur dioxide in 2003 is increased to 2,220 ten thousand tons, and the discharge capacity of nitrogen oxide has reached 1,500 ten thousand tons.
Because on economic structure of China and the basis that social life is based upon home grown energy, and coal accounts for 90% of conventional energy resource proved reserves, therefore, in quite long from now on period, coal will be the main energy sources of China, according to the relevent statistics: if do not take the measure of effectively cutting down, the year two thousand twenty China SO
2Discharge capacity will reach 3,500 ten thousand tons, and the NOx discharge capacity will reach 2,700 ten thousand tons more than.
Nearly 30-40 comes various countries' science to have to be devoted to prevent the desulfurization removing nitric research of acid rain, at present in the world to SO
2Control technology comparative maturity, the industrialized unit that China develops voluntarily also tests successfully and goes into operation.Regard to the emission control of NOx, though domestic place has carried out a series of researchs, and obtained certain progress, but because the flue gas amount of entering is very big, the concentration of NOx is very low in the waste gas, technical difficulty is bigger, does not also find the resolution of technical reasonable, viable economically, a suitable China's national situation at present.
The harmfulness of NOx is just outstanding relatively.Therefore, NOx removes the main contents of being listed in prevention and control of air pollution by industrialized country, and various countries have formulated in succession and contained NOx exhaust gas discharging index, and the discharge capacity of NOx is limited.Along with the raising of the mankind, more and more stricter to containing NOx exhaust gas discharging requirement meeting to environmental requirement.
Be NO more than the NOx90% in the coal-fired flue-gas, the main difficulty that NOx removes is that NO is insoluble in water, so the foothold of the recovery of NOx is the absorption of strengthening NO.
Adsorption method for purifying NO
xAdvantage be: technology is simple, and the purification efficiency height need not to consume chemical substance, and equipment is simple, and is easy to operate.Shortcoming is: because the adsorbents adsorb capacity is little, the quantity of sorbent that needs is big, and equipment is huge, and the adsorbent reactivation difficulty is dealt with improperly and caused secondary pollution easily, and this process is intermittently operated.So the commercial Application of absorption method is not extensive, the flue gas that not too is suitable for coal-burning boiler is handled, and is only applicable to purified treatment and contains NO
xThe waste gas that concentration is lower.
Because selective catalytic reduction and SNCR method all need consume a large amount of NH
3, if can be with NO
xDirectly catalytic decomposition is N
2And O
2, just can reach both pollution abatements, again the purpose of energy savings and resource.With respect to catalytic reduction method, the catalytic decomposition method is removing NO
xMethod in have more attraction.At first, from thermodynamic data, NO
xAt a lower temperature with respect to N
2And O
2Be unsettled, during 298K, the equilibrium constant of NO decomposition reaction under standard state is about 1071 when being about 1015.773K.As seen, direct decomposing N O
xBe fully feasible on thermodynamics; In addition, reaction does not need any reducing agent, and need increase problems such as bulky equipment and investment operating cost height will not exist because of the interpolation reducing agent; In addition, because product is N
2And O
2, can not cause secondary pollution.So the catalytic decomposition method should be simple and the most direct NO
xRemoval method.
To NO
xDecomposition have the catalyst of catalytic action that platinum metal, transition metal, rare earth metal and oxide thereof etc. are arranged.The decomposition efficiency of some catalyst is high but can not be lasting, and main cause is NO
xThe oxygen that decomposes the back generation is difficult for removing from carrier, thereby makes catalysqt deactivation.If replace traditional carrier mass (Al with solid carbon
2O
3And SiO
2Deng) make catalyst, charcoal easily reacts with the surperficial oxygen that adsorbs and generates gaseous material CO, CO
2Deng, oxygen is removed, thereby avoid the activated centre on the catalyst surface to poison because of adsorb oxygen.In addition, solid carbon itself is exactly a reducing agent, and it is easy to NO
xBe reduced to NO or N
2O.But because of course of reaction consumes the charcoal carrier, catalyst life will depend on the depletion rate of charcoal, especially higher gas to oxygen content, and the life-span is shorter, and this method is also in further studying
The key of said method just is the selective reduction of NO.Since in industrial production, combustion product gases composition more complicated, and behind electrostatic precipitation, temperature is 140～150 ℃, dust-laden 100～150mg/m
3, H
2O5～8%, SO
21000～4000ppm, NO300～800ppm, O24～7%, CO
212～15%, N
2About 75%.Can directly utilize the O in the flue gas
2Come oxidation NO, this reaction is a reversible heat release, but because NO concentration is low, reacts very slow, therefore need utilize high activated catalyst to add fast response.SO
2And H
2The existence of O may make catalyst poisoning.
NO in waste gas pollution control and treatment
xBe commonly referred to as NO and NO
2The NO that shows on many rules
x, refer to NO
2(suppose that promptly all NO are converted into NO
2).NO
xBe not only the principal element that acid rain forms, and can form then mist of photochemistry with reaction such as hydrocarbons.NO
2The main harm of in atmosphere another is to help to form O
3, can cause the formation of photochemical fog.
The method that removes NOx in the waste gas now can be divided into two kinds: a kind of is wet method, promptly NOx in the waste gas is converted into NO
3Or NO
2Reclaimed, as prolonging absorption process, chemical absorption method and physical and chemical adsorption method; Another kind is a dry method, promptly makes NOx be converted into the nitrogen that can discharge by reducing agent, and its typical case's representative is a catalytic reduction method, comprises selective catalytic reduction (SCR) and non-selective catalytic reduction (SNCR).
To the different NOx waste gas that contain, need to adopt different improvement methods.It is better to prolong the absorption process removal effect, and absorption liquid can directly return production system, but needs existing apparatus is carried out bigger change.Chemical absorption method handles that NOx waste gas has that product can fully utilize or advantage such as partially recycled, non-secondary pollution, for improving the gas purification degree, controlling qualified discharge is very favorable, can obtain environment and economic double benefit, but consumption of power is big, purification efficiency is low.Though absorption method early has the industrialization report abroad, domesticly still be in the experimental study stage.Catalytic reduction method is the more a kind of method of studying at present, has been mature technology abroad, and in industrial extensive use.But consume a large amount of NH in the catalytic reduction method operation process
3And fuel gas, so that investment and regular job expense are more uneconomical economically than higher.Though some technology have reached very high purification level, be cost to consume a large amount of energy, resource often, and need expensive equipment investment.
China is developing country, and waste gas pollution control and treatment more will be considered its economy and technical conditions, selects that certain economic benefit is arranged, processing method simple to operate is proper.The selectivity catalysis method is administered and is contained NOx waste gas, is the method that generally adopts in the chemical industry production process.Here mainly introduce catalysis method improvement and contain NOx waste gas.
NOx can directly resolve into N by catalyst
2And O
2:
NO(g)→1/2N
2+1/2O
2；ΔG°＝-86.9KJ/mol(25℃)
Nitric plant's vent gas treatment can be in this way.Used catalyst except that noble metal series catalysts such as platinum, base metals such as also available Co, Ni, Cu, Cr.
This is considered to the simplest and gets rid of NO the most completely
xMethod.Owing to do not need reducing agent and oxidant, also be most economical therefore.Although but this decomposition reaction can be carried out on the thermodynamics, and before 50 years just the someone utilize solid catalyst to study this reaction, do not find out practical catalyst so far as yet.Its reason be no matter be decompose generate or emission gases in oxygen can both make catalyst poisoning, hinder the further absorption of NO.
Be applicable to that the catalytic component that NOx decomposes has platinum metal, transition metal, rare earth metal and oxide, exchanging zeolite with metallic ion etc.Noble metals such as Pt and calcium titanium stone type composite oxide at high temperature have higher activity, but are subjected to the influence of oxygen poisoning very big.The transition metal oxide that possesses the 3d electronics is decomposing N O effectively, it is generally acknowledged that the activity of its decomposing N O is relevant with the power of its Lattice Oxygen-intermetallic connecting key, and the oxygen vacancy on surface then is likely the activated centre of decomposing N O.What have application prospect most is molecular sieve (Cu-ZSM-5) through ion-exchange, and this catalyst promptly has higher activity under 300～500 ℃ lower temperature, but at O
2Or SO
2Under the condition of coexistence, the activity of its decomposing N O but descends rapidly.In addition, this catalyst time when 2% steam exists is long unstable.Therefore, the renovation process of coal-fired flue-gas denitrification catalyst is to influence the key factor that catalyst is used.
Summary of the invention
At the problem that present denitrification catalyst regeneration activating technology exists, the invention provides a kind of renovation process and device of catalysis-adsorption agent for flue gas denitrification.
Regenerating unit is made of vertical steam activation resistance furnace, controllable type steam generator or industrial vapor source, device for absorbing tail gas.Vertical steam activation stove comprises at the bottom of bearing at the bottom of dumping pit, heating tube, refractory material heat-insulation layer, safety valve, thermocouple and gauge manifold, window, gas-flow deflector, activation gas inlet, top cover, charging hole, inner core, housing, the sorbent tube, spiracular plate, leg, safety valve connecting pipe, tail gas outlet, the device.
Housing and inner core are cylindrical shape, and ecto-entad is refractory material heat-insulation layer, heating tube successively in the annular space that housing and inner core constitute, and regeneration zone is seated in the inner core.Window, activation gas inlet are set on the top cover, on upper end, the regeneration zone gas-flow deflector is installed in the inner core, activation gas inlet is communicated with by gas-flow deflector with inner core inside, housing sidewall is provided with safety valve, thermocouple and gauge manifold, and safety valve, thermocouple and gauge manifold pass housing, refractory material heat-insulation layer, heating tube, inner core and lead in the inner core.At the lower housing portion sidewall dumping pit is set, dumping pit passes housing, refractory material heat-insulation layer, heating tube, inner core and leads in the inner core.Charging hole and inner core internal communication, bearing at the bottom of the installation sorbent tube at the bottom of the device, spiracular plate is installed on the bearing at the bottom of the sorbent tube, spiracular plate is positioned at tube bottom, safety valve connecting pipe, tail gas outlet are set at the bottom of the device, the tail gas outlet is by spiracular plate and inner core internal communication, and the device back welding connects leg, is used to support activation furnace.
Steam provides by controllable type steam generator or adopts industrial vapor source to provide in the device, be connected in the vertical steam activation resistance furnace by pressure piping, steam pipe enters from furnace upper end, through stove inner vapor diffuser, lead in the catalyst-sorbent regeneration zone, after the discharge of lower end blast pipe.Deliver in the raffinate absorption plant by pipeline, through the liquefaction of steam liquefaction distributor, be convenient to absorb before absorbing.
During catalyst regeneration, activation furnace is heated to 200 ℃～500 ℃ of predetermined temperatures earlier, begin to feed the steam of steam generator or the generation of industrial vapor source then from activation gas porch, through regeneration zone, wherein catalyst-sorbent is carried out steam regeneration stripping, and the steam behind the stripping is discharged to be delivered in the device for absorbing tail gas by pipeline through spiracular plate, outlet again and is absorbed.Tail gas tentatively liquefies and heat exchange through steam liquefaction distributor before absorbing, and is beneficial to tail gas and absorbs.Last absorption liquid enters sewage centralized processing system, harmless emission.
The renovation process of determining the catalysis-adsorption agent preparation is the steam method of reproduction, and processing step is:
To pack in the resistance furnace through the catalyst after the coal-fired flue-gas denitrogenation processing, resistance furnace is warming up to 200 ℃～500 ℃, the feeding temperature is 100 ℃～200 ℃ a steam, control water vapour pressure 0.05MPa～1MPa, make steam pass through catalyst layer in the resistance furnace, with tail gas through 10%～20% Na
2CO
3Solution absorbs, discharges, and this alkali lye absorption plant is connected by heat-resisting acid-proof pipe.
300 ℃～400 ℃ of the temperature of best regeneration, the best recovery time is 20～60min.In practical operation, can regulate operating condition targetedly, reach best denitration effect.The flow of control steam is air speed 1000～2000h
-1, resistance furnace internal pressure 0.05～0.5MPa.
For example, the inventive method can be handled following magnesium oxide-based catalysis-adsorption agent, and this catalysis-adsorption agent adopts wet mixing method preparation, according to following processing step:
(1) pulverizes
The magnesia unslacked finished product is pulverized, be sized to-200 orders (, then omitting this step) if used industrial goods magnesia is crushed to-200 orders; Because of being placed on, magnesia easily absorbs airborne moisture in the air, the magnesium hydroxide of Sheng Chenging also may generate magnesium carbonate with the carbon dioxide in air reaction and lump in addition, so should be with the industrial magnesium oxide pulverize that has lumpd, and be placed in 650 ℃ of muffle furnaces roasting 3 hours, to remove the carbonate of moisture and part.
(2) dissolving
Adding the light calcined magnesia after pulverizing, water is solvent, dissolves uniform MgSO down at 30～50 ℃
4In the mixed liquor of sucdrol flour additive agent, mix, and mixing water transfers to plastic soft condition.Material proportion is counted according to percentage by weight: light calcined magnesia 50%～80%, MgSO
410%～40%, sucdrol powder 0.1%～5%, water 5%～35%.Add moisture what, need suitably, make mixture cross rare and can not granulating and forming too much, resistance was excessive when addition made moulding less, can not press the requirement shape.
(3) moulding
Carry out forming processes with banded extruder, extrude the material of slice state; The magnesium oxide-based catalysis-adsorption agent of preparation adopts cylindrical outer shape, and cylindrical size commonly used has: diameter is 6.4,4.8,3.2,2,1.1mm etc., highly is generally 2～3 times of diameter.The profile of magnesium oxide-based catalysis-adsorption agent and size should be determined according to the requirement of concrete reaction unit.
(4) drying
Under 50～130 ℃ with the dry materials 5～20min of drying box to moulding;
(5) granulate
After drying is good, material is extruded into Φ 2mm and is cut into the cylinder particulate that 5mm grows up little through banded extruder;
(6) roasting
The material of granulating is put into resistance furnace, and with resistance furnace temperature programming to 350～700 ℃, to material activating roasting 2～4h, the control heating rate is 15～25 ℃/minute.Take out the room temperature cooling then, packing is made magnesium oxide-based catalysis-adsorption agent finished product.
According to the catalysis-adsorption agent product of above-mentioned technology preparation, chemical composition is MgO 67%～90%, MgSO according to mass percent
410%～33%.Specific area (BET) is determined as 25～40m
2/ g.Product iodine number 400～550mg/g.The product drum strength is greater than 99%.
Adopt the catalyst of above-mentioned technology preparation to carry out coal-fired flue-gas denitrification treatment process step and technological parameter:
Adsorption tower bed height 1m～6m enters the mouth coal-fired flue-gas and to introduce adsorption tower at the bottom of tower, radially by the catalyst-sorbent bed, and control flue gas air speed 2000～3500h
-1, 30～250 ℃ of temperature, absorption tail gas is discharged after the absorption of tail gas adsorbent equipment.The granularity of magnesium oxide-based catalysis-adsorption agent is determined: according to all wall effects: d≤1/16D, d is the granularity of magnesium oxide-based catalysis-adsorption agent in the formula, and D is generally 0.5m～3m for the reaction tower diameter.The granularity of catalysis-adsorption agent is the long 5～10mm of cylinder, φ 2～5mm.The loading 1m of magnesium oxide-based catalysis-adsorption agent in adsorption tower
3～20m
3
The mensuration of nitric efficiency.
National standard hydrochloride naphthodiamide spectrophotometer method only is suitable for measuring the NO that contains low concentration
xGas, so this paper measures NO
xThe method that concentration adopted is to national standard hydrochloride naphthodiamide spectrophotometer method (GB/T 15435-1995) (handling the back nitrogenous gas) and the NaOH absorption-hydrochloride naphthodiamide AAS of improving one's methods (nitrogenous gas before handling) thereof.
Also adopt Germany to produce hand-held NO analyzer (Kane-May SINGLE GAS ANALGSER SGA) simultaneously, carry out subsidiary, to guarantee the accuracy of data.Measurement result denitration efficiency 80%～99.5%.
Magnesium oxide-based catalysis-adsorption agent is after a period of time is used in denitration, because ash content, the influence of extraneous factors such as other foreign gas, and inactivation.For reaching regeneration effect preferably, the temperature of calcination process is crucial again.The steam thermal regeneration mainly is the hot volatile impurity of deviating from the magnesium oxide-based catalysis-adsorption agent, again the active defective on activated catalyst surface.
From Fig. 3 curve as can be known, activation temperature keeps constant substantially at the clearance of the catalyst n O of 300,400 ℃ of temperature sections, but the clearance of the clearance of the catalyst n O of 200,500 ℃ of temperature sections is obvious downward trend.The regenerative process treatment temperature is remarkable to the denitrogenation influence as can be known, and at 300～400 ℃ of temperature sections, steam is taken away the catalyst surface volatile ingredient, forms new surface-active face within it in portion's structure.During at 200 ℃, steam makes surperficial MgO and steam reaction generation Mg (OH) because temperature is crossed low and formed excessive moisture film at catalyst surface in Control for Kiln Temperature
2And passivation, inactivation; When furnace temperature was 500 ℃, because temperature crosses high water vapor, high temperature dissociated, and the catalyst surface active defective is eliminated in a large number, became inertia and made down active.
Mg among the MgO only has in its oxide+the divalent attitude, and this does not need reduction in the calcination activation process at it, and its activity just showed when there was defective in the MgO surface, and increased with the increase of defective.Therefore for making MgO the Lattice Oxygen defective that may exist occur, feed steam in to its activation process, to destroy its plane of crystal, it is active that it is produced.Simultaneously, it is short that steam activation has the recovery time, the bigger advantage of green strength.
Recovery time is to influence such as Fig. 4 of magnesium oxide-based catalysis-adsorption agent, and 20,30,40min regeneration back denitration effect slightly raises, it is not obvious that the result differs.20min denitration rate is lower slightly, and 30min is the highest, illustrates that the recovery time is little to regeneration effect, and processing reaches certain hour and gets final product.In the process, the component of original deposition is removed, it is big that the micropore of obstruction and mesopore aperture become.Therefore the present invention determine to the magnesium oxide-based catalyst regeneration time be 20～60min.
Magnesium oxide-based catalyst as Fig. 5, has kept the stability of denitrogenation through 6 regeneration backs.This has also illustrated this magnesium oxide-based catalyst feasibility in actual applications.
The catalyst physico-chemical property is analyzed before and after the desorption:
Fourier transform infrared spectroscopy (FTIR) analysis is seen accompanying drawing.
X-ray diffraction after the denitration (XRD) atlas analysis is seen accompanying drawing.
The advantage of renovation process of the present invention is:
1, easy to operate, quick.
2, non-exhaust emission in the regenerative process does not produce secondary pollution.Production capacity is big, equipment resistance is little, efficient is high, operating flexibility is big.
3, the advantage of alternating temperature activation is that heat transfer coefficient is very big, and heating activates fully rapidly, and during the water steam heated, the product after the activation easily reclaims.Catalysis-adsorption agent still can keep high activity through repeatedly regenerating, and has kept the stability of denitrogenation.
Description of drawings
Fig. 1 is the vertical steam activation furnace structure of a present invention schematic diagram;
Fig. 2 is a catalyst regeneration process flow chart of the present invention;
Fig. 3 is the influence (experimental result) of water flowing steam primary recycling 20min temperature to the NO clearance;
Fig. 4 is the influences (experimental result) of 400 ℃ of water flowing steam regeneration primary recycling times to the NO clearance;
Fig. 5 is the influence (experimental result) of 20min400 ℃ of regeneration times of water flowing steam regeneration to the NO clearance;
Fig. 6 catalyst Fourier transform infrared spectroscopy spectrogram, wherein (a) magnesium oxide-based catalysis-adsorption agent new product spectrogram; (b) the denitration spectrogram of once not regenerating; (c) steam regeneration spectrogram after the denitration; (d) spectrogram is carried out in regeneration repeatedly 6 times after the denitration;
Fig. 7 (a) is actual X-ray diffraction (XRD) collection of illustrative plates for for catalyst X-ray diffraction (XRD) collection of illustrative plates; (b) analyze collection of illustrative plates for the curve crest.
Among the figure: the 1-dumping pit; The 2-heating tube; 3-refractory material heat-insulation layer; 4-safety valve, thermocouple and gauge manifold; The 5-window; The 6-gas-flow deflector; 7-activation gas inlet; The 8-top cover; The 9-charging hole; The 10-inner core; The 11-housing; Bearing at the bottom of the 12-sorbent tube; The 13-spiracular plate; The 14-leg; The 15-safety valve connecting pipe; The outlet of 16-tail gas; At the bottom of the 17-device; The 18-regeneration zone.
The specific embodiment
As shown in Figure 1, vertical steam activation stove comprises at the bottom of bearing 12 at the bottom of dumping pit 1, heating tube 2, refractory material heat-insulation layer 3, safety valve, thermocouple and gauge manifold 4, window 5, gas-flow deflector 6, activation gas inlet 7, top cover 8, charging hole 9, inner core 10, housing 11, the sorbent tube, spiracular plate 13, leg 14, safety valve connecting pipe 15, tail gas outlet 16, the device 17.
Housing 11 and inner core 10 are cylindrical shape, and ecto-entad is refractory material heat-insulation layer 3, heating tube 2 successively in the annular space that housing 11 and inner core 10 constitute, and regeneration zone 18 is seated in the inner core 10.Window 5, activation gas inlet 7 are set on the top cover 8, gas-flow deflector 6 is installed on upper end, the regeneration zone 18 in the inner core 10, activation gas inlet 7 is communicated with by gas-flow deflector 6 with inner core 10 inside, housing 11 sidewalls are provided with safety valve, thermocouple and gauge manifold 4, and safety valve, thermocouple and gauge manifold 4 pass housing 11, refractory material heat-insulation layer 3, heating tube 2, inner core 10 and lead in the inner core 10.At housing 11 lower sides dumping pit 1 is set, dumping pit 1 passes housing 11, refractory material heat-insulation layer 3, heating tube 2, inner core 10 and leads in the inner core 10.Charging hole 9 and inner core 10 internal communication, bearing 12 at the bottom of sorbent tube being installed in 17 at the bottom of the device, spiracular plate 13 is installed on the bearing 12 at the bottom of the sorbent tube, spiracular plate 13 is positioned at inner core 10 bottoms, safety valve connecting pipe 15, tail gas outlet 16 are set on 17 at the bottom of the device, tail gas outlet 16 is by spiracular plate 13 and inner core 10 internal communication, and the device back welding connects leg 14, is used to support activation furnace.
Prepare catalyst according to following processing step:
(1) pulverizes
The magnesia unslacked finished product is pulverized, be sized to-200 orders; Because of being placed on, magnesia easily absorbs airborne moisture in the air, the magnesium hydroxide of Sheng Chenging also may generate magnesium carbonate with the carbon dioxide in air reaction and lump in addition, so should be with the industrial magnesium oxide pulverize that has lumpd, and be placed in 650 ℃ of muffle furnaces roasting 3 hours, to remove the carbonate of moisture and part.
(2) dissolving
Adding the light calcined magnesia after pulverizing, water is solvent, dissolves uniform MgSO down at 40 ℃
4In the mixed liquor of sucdrol flour additive agent, mix, and mixing water transfers to plastic soft condition.Material proportion is counted according to percentage by weight: light calcined magnesia 60%, MgSO
430%, sucdrol powder 2%, water 8%.
(3) moulding
Carry out forming processes with banded extruder, extrude the material of slice state; The magnesium oxide-based catalysis-adsorption agent of preparation adopts cylindrical outer shape, and cylindrical size has: diameter is 6.4,4.8,3.2,2 or 1.1mm, highly is 2 times of diameter.The profile of magnesium oxide-based catalysis-adsorption agent and size should be determined according to the requirement of concrete reaction unit.
(4) drying
Under 80 ℃ with the dry materials 15min of drying box to moulding;
(5) granulate
After drying is good, material is extruded into Φ 2mm and is cut into the cylinder particulate that 5mm grows up little through banded extruder;
(6) roasting
The material of granulating is put into resistance furnace, and with resistance furnace temperature programming to 500 ℃, to material activating roasting 3h, the control heating rate is 20 ℃/minute.Take out the room temperature cooling then, packing is made magnesium oxide-based catalysis-adsorption agent finished product.
Product specific area of the present invention (BET) is determined as 30m
2/ g.
Record product iodine number 480mg/g of the present invention.
Record product drum strength of the present invention greater than 99%.
Adopt the catalyst of above-mentioned technology preparation to carry out coal-fired flue-gas denitrification treatment process step and technological parameter:
Adsorption tower bed height 3m enters the mouth coal-fired flue-gas and to introduce adsorption tower at the bottom of tower, radially by the catalyst-sorbent bed, and control flue gas air speed 2800h
-1, 150 ℃ of temperature, absorption tail gas is discharged after the absorption of tail gas adsorbent equipment.The granularity of magnesium oxide-based catalysis-adsorption agent is determined: according to all wall effects: d≤1/16D, d is the granularity of magnesium oxide-based catalysis-adsorption agent in the formula, and D is the reaction tower diameter.The granularity of catalysis-adsorption agent is the long 5～10mm of cylinder, φ 2～5mm.The loading 15m of magnesium oxide-based catalysis-adsorption agent in adsorption tower
3
Measurement result denitration efficiency 99%.
The renovation process of determining magnesium oxide-based catalysis-adsorption agent preparation is the steam method of reproduction, and processing step is:
To pack in the resistance furnace through the catalyst after the coal-fired flue-gas denitrogenation processing, resistance furnace is warming up to 450 ℃, and feed temperature and be 150 ℃ steam, control water vapour pressure 0.3MPa makes steam pass through catalyst layer in the resistance furnace, with tail gas through 15% Na
2CO
3Solution absorbs, discharges, and this alkali lye absorption plant is connected by heat-resisting acid-proof pipe.
Recovery time is 40min.The flow of control steam is air speed 1500h
-1, resistance furnace internal pressure 0.2MPa.Utilize the catalysis-adsorption agent after regenerating to carry out the coal-fired flue-gas denitrogenation processing, nitric efficiency 99%.
Prepare catalyst according to following processing step:
(1) pulverizes
The magnesia unslacked finished product is pulverized, be sized to-200 orders; Because of being placed on, magnesia easily absorbs airborne moisture in the air, the magnesium hydroxide of Sheng Chenging also may generate magnesium carbonate with the carbon dioxide in air reaction and lump in addition, so should be with the industrial magnesium oxide pulverize that has lumpd, and be placed in 650 ℃ of muffle furnaces roasting 3 hours, to remove the carbonate of moisture and part.
(2) dissolving
Adding the light calcined magnesia after pulverizing, water is solvent, dissolves uniform MgSO down at 50 ℃
4In the mixed liquor of sucdrol flour additive agent, mix, and mixing water transfers to plastic soft condition.Material proportion is counted according to percentage by weight: light calcined magnesia 80%, MgSO
410%, sucdrol powder 3%, water 7%.
(3) moulding
Carry out forming processes with banded extruder, extrude the material of slice state; The magnesium oxide-based catalysis-adsorption agent of preparation adopts cylindrical outer shape, and cylindrical size has: diameter is 6.4,4.8,3.2,2 or 1.1mm, highly is 3 times of diameter.The profile of magnesium oxide-based catalysis-adsorption agent and size should be determined according to the requirement of concrete reaction unit.
(4) drying
Under 50 ℃ with the dry materials 20min of drying box to moulding;
(5) granulate
After drying is good, material is extruded into Φ 2mm and is cut into the cylinder particulate that 5mm grows up little through banded extruder;
(6) roasting
The material of granulating is put into resistance furnace, and with resistance furnace temperature programming to 700 ℃, to material activating roasting 2h, the control heating rate is 25 ℃/minute.Take out the room temperature cooling then, packing is made magnesium oxide-based catalysis-adsorption agent finished product.
Product specific area of the present invention (BET) is determined as 40m
2/ g.
Record product iodine number 550mg/g of the present invention.
Record product drum strength of the present invention greater than 99%.
Adopt the catalyst of above-mentioned technology preparation to carry out coal-fired flue-gas denitrification treatment process step and technological parameter:
Adsorption tower bed height 6m enters the mouth coal-fired flue-gas and to introduce adsorption tower at the bottom of tower, radially by the catalyst-sorbent bed, and control flue gas air speed 3500h
-1, 250 ℃ of temperature, absorption tail gas is discharged after the absorption of tail gas adsorbent equipment.The granularity of magnesium oxide-based catalysis-adsorption agent is determined: according to all wall effects: d≤1/16D, d is the granularity of magnesium oxide-based catalysis-adsorption agent in the formula, and D is the reaction tower diameter.The granularity of catalysis-adsorption agent is the long 5～10mm of cylinder, φ 2～5mm.The loading 20m of magnesium oxide-based catalysis-adsorption agent in adsorption tower
3
Measurement result denitration efficiency 99.5%.
The renovation process of determining magnesium oxide-based catalysis-adsorption agent preparation is the steam method of reproduction, and processing step is:
To pack in the resistance furnace through the catalyst after the coal-fired flue-gas denitrogenation processing, resistance furnace is warming up to 200 ℃, and feed temperature and be 100 ℃ steam, controlled pressure steam 0.06MPa makes steam pass through catalyst layer in the resistance furnace, with tail gas through 10% Na
2CO
3Solution absorbs, discharges, and this alkali lye absorption plant is connected by heat-resisting acid-proof pipe.Recovery time is 60min.In practical operation, can regulate operating condition targetedly, reach best denitration effect.The flow of control steam is air speed 1000h
-1, resistance furnace internal pressure 0.05MPa.Utilize the catalysis-adsorption agent after regenerating to carry out the coal-fired flue-gas denitrogenation processing, nitric efficiency 97.9%.
Prepare catalyst according to following processing step:
(1) pulverizes
The magnesia unslacked finished product is pulverized, be sized to-200 orders; Because of being placed on, magnesia easily absorbs airborne moisture in the air, the magnesium hydroxide of Sheng Chenging also may generate magnesium carbonate with the carbon dioxide in air reaction and lump in addition, so should be with the industrial magnesium oxide pulverize that has lumpd, and be placed in 650 ℃ of muffle furnaces roasting 3 hours, to remove the carbonate of moisture and part.
(2) dissolving
Adding the light calcined magnesia after pulverizing, water is solvent, dissolves uniform MgSO down at 30 ℃
4In the mixed liquor of sucdrol flour additive agent, mix, and mixing water transfers to plastic soft condition.Material proportion is counted according to percentage by weight: light calcined magnesia 50%, MgSO
433%, sucdrol powder 3%, water 14%.
(3) moulding
Carry out forming processes with banded extruder, extrude the material of slice state; The magnesium oxide-based catalysis-adsorption agent of preparation adopts cylindrical outer shape, cylindrical size: diameter is 6.4,4.8,3.2,2 or 1.1mm, highly is 3 times of diameter.The profile of magnesium oxide-based catalysis-adsorption agent and size should be determined according to the requirement of concrete reaction unit.
(4) drying
Under 130 ℃ with the dry materials 5min of drying box to moulding;
(5) granulate
After drying is good, material is extruded into Φ 2mm and is cut into the cylinder particulate that 5mm grows up little through banded extruder;
(6) roasting
The material of granulating is put into resistance furnace, and with resistance furnace temperature programming to 350 ℃, to material activating roasting 4h, the control heating rate is 15 ℃/minute.Take out the room temperature cooling then, packing is made magnesium oxide-based catalysis-adsorption agent finished product.
Product specific area of the present invention (BET) is determined as 25m
2/ g.
Record product iodine number 400mg/g of the present invention.
Record product drum strength of the present invention greater than 99%.
Adopt the catalyst of above-mentioned technology preparation to carry out coal-fired flue-gas denitrification treatment process step and technological parameter:
Adsorption tower bed height 1m enters the mouth coal-fired flue-gas and to introduce adsorption tower at the bottom of tower, radially by the catalyst-sorbent bed, and control flue gas air speed 2000h
-1, 30 ℃ of temperature, absorption tail gas is discharged after the absorption of tail gas adsorbent equipment.The granularity of magnesium oxide-based catalysis-adsorption agent is determined: according to all wall effects: d≤1/16D, d is the granularity of magnesium oxide-based catalysis-adsorption agent in the formula, and D is the reaction tower diameter.The granularity of catalysis-adsorption agent is the long 5～10mm of cylinder, φ 2～5mm.The loading 1m of magnesium oxide-based catalysis-adsorption agent in adsorption tower
3
Measurement result denitration efficiency 88%.
The renovation process of determining magnesium oxide-based catalysis-adsorption agent preparation is the steam method of reproduction, and processing step is:
To pack in the resistance furnace through the catalyst after the coal-fired flue-gas denitrogenation processing, resistance furnace is warming up to 500 ℃, and feed temperature and be 200 ℃ steam, control water vapour pressure 1MPa makes steam pass through catalyst layer in the resistance furnace, with tail gas through 20% Na
2CO
3Solution absorbs, discharges, and this alkali lye absorption plant is connected by heat-resisting acid-proof pipe.Recovery time is 20min.In practical operation, can regulate operating condition targetedly, reach best denitration effect.The flow of control steam is air speed 2000h
-1, resistance furnace internal pressure 0.5MPa.Utilize the catalysis-adsorption agent after regenerating to carry out the coal-fired flue-gas denitrogenation processing, nitric efficiency 98.5%.
Claims (6)
1, a kind of renovation process of catalysis-adsorption agent for flue gas denitrification, it is characterized in that adopting the steam method of reproduction, to pack in the resistance furnace through the catalysis-adsorption agent after the coal-fired flue-gas denitrogenation processing, resistance furnace is warming up to 200 ℃～500 ℃, the feeding temperature is 100 ℃～200 ℃ a steam, control water vapour pressure 0.05MPa～1MPa, the time is 20～60min, the flow of control steam is air speed 1000～2000h
-1, resistance furnace internal pressure 0.05～0.5Mpa makes steam pass through catalyst layer in the resistance furnace, with tail gas through 10%～20% Na
2CO
3Solution absorbs, discharges.
2, the resistance furnace of the renovation process of the described catalysis-adsorption agent for flue gas denitrification of claim 1 employing, it is characterized in that this resistance furnace is vertical steam activation resistance furnace, housing and inner core are cylindrical shape, and ecto-entad is refractory material heat-insulation layer, heating tube successively in the annular space that housing and inner core constitute.
3, according to the described resistance furnace of claim 2, it is characterized in that being provided with on the top cover window, activation gas inlet, gas-flow deflector is installed in the upper end in the inner core, and activation gas inlet is communicated with by gas-flow deflector with inner core inside.
4, according to the described resistance furnace of claim 2, it is characterized in that housing sidewall is provided with safety valve, thermocouple and gauge manifold, safety valve, thermocouple and gauge manifold pass housing, refractory material heat-insulation layer, heating tube, inner core and lead in the inner core.
5, according to the described resistance furnace of claim 2, it is characterized in that dumping pit being set at the lower housing portion sidewall, dumping pit passes housing, refractory material heat-insulation layer, heating tube, inner core and leads in the inner core.
6, according to the described resistance furnace of claim 2, it is characterized in that at the bottom of the device installing bearing at the bottom of the sorbent tube, spiracular plate is installed on the bearing at the bottom of the sorbent tube, spiracular plate is positioned at tube bottom, safety valve connecting pipe, tail gas outlet are set at the bottom of the device, and tail gas exports by spiracular plate and inner core internal communication.
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106310943A (en) * | 2016-08-31 | 2017-01-11 | 上海交通大学 | Device for regenerating sodium sulfite desulphurization liquid and recycling sulfur dioxide with sodium sulfite desulphurization liquid and application of device |
| CN114233282A (en) * | 2021-12-22 | 2022-03-25 | 河南省科学院同位素研究所有限责任公司 | High-efficient zero radioactivity emission well logging tracer preparation system |
| CN114904386A (en) * | 2021-02-08 | 2022-08-16 | 中国石油化工股份有限公司 | Organic waste gas treatment device and use method thereof |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB0104682D0 (en) * | 2001-02-26 | 2001-04-11 | Johnson Matthey Plc | Gas treatment using ammonia |
| JP4578048B2 (en) * | 2002-06-21 | 2010-11-10 | 中国電力株式会社 | Denitration catalyst regeneration method |
| US20040265201A1 (en) * | 2003-06-25 | 2004-12-30 | Norman Dale Brinkman | NOx removal system |
| US7213395B2 (en) * | 2004-07-14 | 2007-05-08 | Eaton Corporation | Hybrid catalyst system for exhaust emissions reduction |
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2006
- 2006-12-30 CN CNB2006101558487A patent/CN100408186C/en not_active Expired - Fee Related
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106310943A (en) * | 2016-08-31 | 2017-01-11 | 上海交通大学 | Device for regenerating sodium sulfite desulphurization liquid and recycling sulfur dioxide with sodium sulfite desulphurization liquid and application of device |
| CN106310943B (en) * | 2016-08-31 | 2018-11-16 | 上海交通大学 | A kind of sodium sulfite desulfurization regeneration and recycling sulfur dioxide device and application |
| CN114904386A (en) * | 2021-02-08 | 2022-08-16 | 中国石油化工股份有限公司 | Organic waste gas treatment device and use method thereof |
| CN114904386B (en) * | 2021-02-08 | 2023-08-08 | 中国石油化工股份有限公司 | Organic waste gas treatment device and application method thereof |
| CN114233282A (en) * | 2021-12-22 | 2022-03-25 | 河南省科学院同位素研究所有限责任公司 | High-efficient zero radioactivity emission well logging tracer preparation system |
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