CN109453783A - A kind of regeneration fume from catalytic cracking desulphurization catalyst and preparation method thereof - Google Patents

A kind of regeneration fume from catalytic cracking desulphurization catalyst and preparation method thereof Download PDF

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CN109453783A
CN109453783A CN201811425042.4A CN201811425042A CN109453783A CN 109453783 A CN109453783 A CN 109453783A CN 201811425042 A CN201811425042 A CN 201811425042A CN 109453783 A CN109453783 A CN 109453783A
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preparation
magnesium
manganese
added dropwise
desulphurization catalyst
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陈伟
卢春喜
范怡平
闫子涵
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Xinchun (shanghai) Environmental Protection Technology Co Ltd
China University of Petroleum Beijing
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Xinchun (shanghai) Environmental Protection Technology Co Ltd
China University of Petroleum Beijing
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/005Spinels
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8603Removing sulfur compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

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Abstract

The present invention provides a kind of regeneration fume from catalytic cracking desulphurization catalysts and preparation method thereof.This method comprises: being slowly added dropwise the mixed solution that magnesium salts and aluminium salt are prepared in sodium hydroxide and the mixed solution of sodium carbonate preparation, it is stirred to react nucleation crystallization after being added dropwise to complete, obtains magnesium aluminate spinel;The mixed solution that manganese salt, magnesium salts and aluminium salt are prepared is slowly added dropwise in sodium hydroxide and the mixed solution of sodium carbonate preparation, nucleation crystallization is stirred to react after being added dropwise to complete, obtains manganese magnesia-alumina hydrotalcite;Magnesium aluminate spinel, manganese magnesia-alumina hydrotalcite, cerous nitrate, copper nitrate and boehmite are uniformly mixed and obtain mixture, mixture is continuously sprayed into hydrochloric acid solution during continuous rolling, sieving obtains small spherical particles;It is roasted to obtain the regeneration fume from catalytic cracking desulphurization catalyst after drying.Its SOx removal efficiency with higher and preferable regenerability, desulfurization degree in regeneration fume from catalytic cracking are up to 99.5%, and regenerability is up to 100%.

Description

A kind of regeneration fume from catalytic cracking desulphurization catalyst and preparation method thereof
Technical field
The invention belongs to environmental protection catalyst technical fields, and in particular to a kind of regeneration fume from catalytic cracking desulphurization catalyst and Preparation method.
Background technique
Catalytic cracking is important one of the secondary processing process of oil plant.Catalytic cracking unit is mainly by reactor and again Raw device composition.Under the effect of the catalyst, raw material is processed into required product in catalyst cracker, is catalyzed in reaction process Agent is inactivated because of coking, and the catalyst fluidization of inactivation carries out coke burning regeneration to regenerator, and then Returning reactor continues to urge Change reaction.During catalytic cracking reaction, the partial vulcanization object in raw material is deposited on a catalyst, when catalyst regeneration, Sulphides burn on catalyst forms sulfur oxide (SOx) with flue gas emission.Oxysulfide SOx not only seriously pollutes ring Border can also be acted on the vapor in flue gas, and condensation generates acid solution on wall, cause heavy corrosion to equipment.Therefore, How the discharge amount of in regeneration fume from catalytic cracking SOx is reduced, it has also become urgent problem to be solved.
The main method for reducing SOx discharge in catalytic cracking regenerator at present is as follows: first is that carrying out to catalytically cracked material Weighted BMO spaces, as ZL201510769249.3, ZL201410766839.6, ZL201210440586.4, ZL201110156347.1 etc..Although catalytically cracked material weighted BMO spaces can be effectively reduced the row of catalytic cracking flue gas SOx It puts, but still cannot reach emission request, and cat feed hydrotreating unit investment is very high, limits this The application of method.Second is that using catalytic cracking regeneration flue gas sulphur transfer agent in catalytic cracking process, such as ZL201510109947.0、ZL201210443822.8、ZL201210349980.7、ZL201110029268.4、 ZL201110328746.1 etc..The SOx content in flue gas can be effectively reduced in this method, and SOx removal efficiency is 50-70%, still Higher and higher with discharge standard, regeneration flue gas sulphur transfer agent has been difficult to meet discharge standard requirement.Third is that catalytic cracking Regenerated flue gas carries out wet desulphurization, and the method being most widely used at present, as ZL201410092858.5, ZL201410590103.8, ZL201610031292.4, ZL201120070516.5 etc..But wet process of FGD was being applied Find that it easily causes " blue smoke (SO in journey3) ", " white cigarette (vapor) " and brine waste discharge, formed secondary pollution.
Compared with fixed bed reactors, moving bed can realize particle circular regeneration and continuous circulate operation;And compared to stream Change bed, moving bed particle solid holdup is high, two-phase contacting efficiency is higher.But operated using moving bed, not only to guarantee desulfurizing agent Desulfurization effect, while higher requirement also proposed to its mechanical performance.Moving bed is thus used for the correlation of flue gas desulfurization Technology is extremely limited, as used active Jiaozhuo in the technique using the proposition of ZL201410111683.8, ZL 200610017066.7 For adsorbent, ZL201220236757.7 is in light filler ball surface layer " carrying " desulfurizing agent, and the then base of ZL 200720066552.8 In the optimization of the moving bed import and export mix, these are not related to the preparation of desulfurizing agent.Therefore, a kind of suitable for movable bed dress is developed The regeneration fume from catalytic cracking desulphurization catalyst set has great importance.
Summary of the invention
Based on problem of the existing technology, the purpose of the present invention is to provide a kind of high-temperature catalytics suitable for moving bed Cracking regeneration flue gas desulfurization catalyst and preparation method thereof.The regeneration fume from catalytic cracking desulphurization catalyst under the high temperature conditions can Regeneration fume from catalytic cracking SOx is enough removed, there is very high removal efficiency, and " blue smoke ", " white cigarette " can be eliminated and contained The discharge of salt waste water avoids the generation of secondary pollution.
On the one hand, the present invention provides a kind of preparation method of regeneration fume from catalytic cracking desulphurization catalyst, and this method includes Following steps:
The mixed solution that magnesium salts and aluminium salt are prepared is slowly added dropwise in the mixing of sodium hydroxide and sodium carbonate preparation step 1 In solution, it is stirred to react nucleation crystallization after being added dropwise to complete, obtains magnesium aluminate spinel;
The mixed solution that manganese salt, magnesium salts and aluminium salt are prepared is slowly added dropwise in sodium hydroxide and sodium carbonate preparation step 2 Mixed solution in, nucleation crystallization is stirred to react after being added dropwise to complete, obtains manganese magnesia-alumina hydrotalcite;
Magnesium aluminate spinel, manganese magnesia-alumina hydrotalcite, cerous nitrate, copper nitrate and boehmite are uniformly mixed by step 3 Mixture is obtained, mixture is continuously sprayed into hydrochloric acid solution during continuous rolling, sieving obtains small spherical particles;
Step 4 will be roasted to obtain the regeneration fume from catalytic cracking desulphurization catalyst after small spherical particles drying.
In above-mentioned preparation method, it is preferable that in step 1, in the mixed solution of magnesium salts and aluminium salt preparation, with metal The molar ratio of oxide meter, the magnesium salts and the aluminium salt is (1-5): 1.
In above-mentioned preparation method, it is preferable that the magnesium salts includes one of magnesium nitrate, magnesium chloride and magnesium sulfate or more Kind;One of the aluminium salt aluminum nitrate, aluminium chloride and aluminum sulfate are a variety of.
In above-mentioned preparation method, it is preferable that in step 1, in the mixed solution that sodium hydroxide and sodium carbonate are prepared, The concentration of the sodium hydroxide is 3-5mol/L, and the concentration of the sodium carbonate is 0.15-0.25mol/L, and the sodium hydroxide Solution with the sodium carbonate is isometric mixing.
In above-mentioned preparation method, it is preferable that in step 2, in the mixed solution that manganese salt, magnesium salts and aluminium salt are prepared, with Metal oxide meter, the molar ratio of the manganese salt, the magnesium salts and the aluminium salt are (0.01-0.2): (1-4.5): 1.
In above-mentioned preparation method, it is preferable that the manganese salt includes manganese nitrate and/or manganese sulfate;The magnesium salts includes nitre One of sour magnesium, magnesium chloride, magnesium sulfate and magnesium acetate are a variety of;The aluminium salt includes in aluminum nitrate, aluminium chloride and aluminum sulfate It is one or more.
In above-mentioned preparation method, it is preferable that in step 2, in the mixed solution that sodium hydroxide and sodium carbonate are prepared, The concentration of the sodium hydroxide is 3-5mol/L, and the concentration of the sodium carbonate is 0.1-0.2mol/L, and the sodium hydroxide and The solution of the sodium carbonate is isometric mixing.
In above-mentioned preparation method, it is preferable that in step 3, mixture is continuously sprayed salt during continuous rolling Acid solution, sieving obtain small spherical particles method particularly includes:
Mixture is even added in turntable bowling machine, hydrochloric acid solution is sprayed into turntable bowling machine using sprayer, By the continuous penetrating of the continuous rolling and hydrochloric acid solution of turntable bowling machine, so that the material of mixture is gradually grown up balling-up, pass through Screening obtains the small spherical particles of 0.2-2.5mm partial size.
In above-mentioned preparation method, it is preferable that the magnesium aluminate spinel, the manganese magnesia-alumina hydrotalcite, the cerous nitrate, The copper nitrate and the dosage for intending thin water aluminium meet in the desulphurization catalyst being prepared, with metal oxide mass content For 100% meter, the Al of MgO, 30%-55% including 25%-50%2O3, 7.5%-15% CeO2, 0.5%-2% MnO2 With the CuO of 1%-5%.
In above-mentioned preparation method, it is preferable that the concentration of the hydrochloric acid solution is 18%.
In above-mentioned preparation method, it is preferable that in step 1, dropping temperature is 50-70 DEG C, time for adding 0.2- 0.5h。
In above-mentioned preparation method, it is preferable that control solution ph is 8-10 during being added dropwise.
In above-mentioned preparation method, it is preferable that the time being stirred to react after being added dropwise to complete is 4-18h.
In above-mentioned preparation method, it is preferable that further include cooling, suction filtration, washing to neutral and baking after being stirred to react Dry step;It is further preferred that drying temperature is 150 DEG C.
In above-mentioned preparation method, it is preferable that in step 2, dropping temperature is 60-80 DEG C, time for adding 0.4- 1h。
In above-mentioned preparation method, it is preferable that control solution ph is 8-10 during being added dropwise.
In above-mentioned preparation method, it is preferable that the time being stirred to react after being added dropwise to complete is 4-20h.
In above-mentioned preparation method, it is preferable that further include cooling, suction filtration, washing to neutral and baking after being stirred to react Dry step;Preferably, drying temperature is 150 DEG C.
In above-mentioned preparation method, it is preferable that in step 4, the temperature that the small spherical particles are dried is 120- 150 DEG C, drying time 5-12h.
In above-mentioned preparation method, it is preferable that the temperature roasted is 700-850 DEG C, calcining time 3-12h.
On the other hand, the present invention also provides a kind of regeneration fume from catalytic cracking desulphurization catalyst, the desulphurization catalyst is It is prepared by the preparation method.
In above-mentioned desulphurization catalyst, it is preferable that in the desulphurization catalyst, be with metal oxide mass content 100% meter, the desulphurization catalyst includes the Al of MgO, 30%-55% of 25%-50%2O3, 7.5%-15% CeO2、 The MnO of 0.5%-2%2With the CuO of 1%-5%.
Beneficial effects of the present invention:
Regeneration fume from catalytic cracking desulphurization catalyst provided by the invention has higher content of MgO, can effectively improve The desulfuration efficiency of catalyst;In the preparation method of the desulphurization catalyst, boehmite is acidified, improves desulfurization catalyst The intensity of agent small spherical particles;And contain boehmite and manganese magnesia-alumina hydrotalcite in small spherical particles, enrich the micro- of catalyst Type structure improves the specific surface area of catalyst;The desulphurization catalyst is applied in regeneration fume from catalytic cracking, is had higher SOx removal efficiency and preferable regenerability, desulfurization degree be up to 99.5%, regenerability is up to 100%.
Specific embodiment
In order to which technical characteristic of the invention, purpose and beneficial effect are more clearly understood, now to skill of the invention Art scheme carries out described further below, but should not be understood as that limiting the scope of the invention.
Embodiment 1
The present embodiment provides a kind of preparation methods of regeneration fume from catalytic cracking desulphurization catalyst comprising following steps:
Step 1, aluminum-spinel (MgAl2O4) preparation:
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 44.5g of O, 114.0g2CO3, stirred in 65 DEG C Uniformly, the H containing 1500g is added thereto2Mg (the NO of O, 108.5g3)2·6H2Al (the NO of O, 93.5g3)3·9H2O's is molten Liquid, time for adding 0.6h continue to stir into core crystallization 15h after dripping, and then, cooling, suction filtration is washed to neutrality and dried It is dry, obtain magnesium aluminate spinel A1.
Step 2, the preparation of manganese magnesia-alumina hydrotalcite (MnMgAl-LDH):
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 53.0g of O, 126.0g2CO3, stirred in 75 DEG C Uniformly, the H containing 1500g is added thereto2Mn (the NO of O, 7.5g3)2·4H2Mg (the NO of O, 285.0g3)2·6H2O, Al (the NO of 123.5g3)3·9H2The solution of O, time for adding 0.7h continue to stir into core crystallization 18h after dripping, then, Cooling, suction filtration is washed to neutrality simultaneously, obtains manganese magnesia-alumina hydrotalcite B1.
Step 3, the acquisition of regeneration fume from catalytic cracking desulphurization catalyst:
By the Ce (NO of 42.5g magnesium aluminate spinel A1,27.3g manganese magnesia-alumina hydrotalcite B1,70.0g3)·6H2O, 22.0g's Cu(NO3)2·6H2O and boehmite 97.0g is added to after mixing to be added in turntable bowling machine, using sprayer to turn Disk bowling machine sprays into 18% dilute hydrochloric acid solution.By the continuous penetrating of the continuous rolling and dilute hydrochloric acid of bowling machine, material in pot It gradually grows up balling-up, it is 8 hours dry at 120 DEG C by screening selection 1.0-1.5mm partial size bead, it is small that 5 are roasted at 750 DEG C When, purpose product regeneration fume from catalytic cracking desulphurization catalyst is obtained, which is named as S1.With metal oxide matter Measuring content is 100% meter, and desulphurization catalyst S1 includes 35.0% MgO, 51.6% Al2O3, 10.8% CeO2, 0.6% MnO2With 2.0% CuO.
Embodiment 2
The present embodiment provides a kind of preparation methods of regeneration fume from catalytic cracking desulphurization catalyst comprising following steps:
Step 1, aluminum-spinel (MgAl2O4) preparation:
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 44.5g of O, 114.0g2CO3, stirred in 65 DEG C Uniformly, the H containing 1500g is added thereto2Mg (the NO of O, 108.5g3)2·6H2Al (the NO of O, 93.5g3)3·9H2O's is molten Liquid, time for adding 0.6h continue to stir into core crystallization 18h after dripping, and then, cooling, suction filtration is washed to neutrality and dried It is dry, obtain magnesium aluminate spinel A2.
Step 2, the preparation of manganese magnesia-alumina hydrotalcite (MnMgAl-LDH):
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 53.0g of O, 126.0g2CO3, stirred in 75 DEG C Uniformly, the H containing 1500g is added thereto2Mn (the NO of O, 9.5g3)2·4H2Mg (the NO of O, 262.4g3)2·6H2O, Al (the NO of 123.5g3)3·9H2The solution of O, time for adding 0.7h continue to stir into core crystallization 18h after dripping, then, Cooling, suction filtration is washed to neutrality simultaneously, obtains manganese magnesia-alumina hydrotalcite B2.
Step 3, the acquisition of regeneration fume from catalytic cracking desulphurization catalyst:
By the Ce (NO of manganese the magnesia-alumina hydrotalcite B2,68.0g of the magnesium aluminate spinel A2,39.4g of 56.2g3)·6H2O, Cu (the NO of 24.0g3)2·6H2The boehmite of O and 107.0g is added to after mixing to be added in turntable bowling machine, is used Sprayer sprays into 18% dilute hydrochloric acid solution to turntable bowling machine.Pass through the continuous spray of the continuous rolling and dilute hydrochloric acid of bowling machine Entering, material is gradually grown up balling-up in pot, and it is 12 hours dry at 130 DEG C by screening selection 1.5-2.0mm partial size bead, It is roasted 7 hours at 800 DEG C, obtains purpose product regeneration fume from catalytic cracking desulphurization catalyst, which is named as S2. It is in terms of 100% by metal oxide mass content, desulphurization catalyst S2 includes 42% MgO, 45% Al2O3, 8.0% CeO2, 1.0% MnO2With 4.0% CuO.
Embodiment 3
The present embodiment provides a kind of preparation methods of regeneration fume from catalytic cracking desulphurization catalyst comprising following steps:
Step 1, aluminum-spinel (MgAl2O4) preparation:
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 44.5g of O, 114.0g2CO3, stirred in 70 DEG C Uniformly, the H containing 1500g is added thereto2Mg (the NO of O, 108.5g3)2·6H2Al (the NO of O, 93.5g3)3·9H2O's is molten Liquid, time for adding 0.6h continue to stir into core crystallization 18h after dripping, and then, cooling, suction filtration is washed to neutrality and dried It is dry, obtain magnesium aluminate spinel A3.
Step 2, the preparation of manganese magnesia-alumina hydrotalcite (MnMgAl-LDH):
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 53.0g of O, 126.0g2CO3, stirred in 75 DEG C Uniformly, the H containing 1500g is added thereto2Mn (the NO of O, 9.5g3)2·4H2Mg (the NO of O, 346.2g3)2·6H2O, Al (the NO of 123.5g3)3·9H2The solution of O, time for adding 1.0h continue to stir into core crystallization 20h after dripping, then, Cooling, suction filtration is washed to neutrality simultaneously, obtains manganese magnesia-alumina hydrotalcite B3.
Step 3, the acquisition of regeneration fume from catalytic cracking desulphurization catalyst:
By the Ce (NO of manganese the magnesia-alumina hydrotalcite B3,55.0g of the magnesium aluminate spinel A3,64.2g of 36.8g3)·6H2O, Cu (the NO of 32.0g3)2·6H2The boehmite of O and 85.0g is added to after mixing to be added in turntable bowling machine, is used Sprayer sprays into 18% dilute hydrochloric acid solution to turntable bowling machine.Pass through the continuous spray of the continuous rolling and dilute hydrochloric acid of bowling machine Entering, material is gradually grown up balling-up in pot, and it is 10 hours dry at 150 DEG C by screening selection 1.0-1.5mm partial size bead, It is roasted 6 hours at 850 DEG C, obtains purpose product regeneration fume from catalytic cracking desulphurization catalyst, which is named as S3. It is in terms of 100% by metal oxide mass content, desulphurization catalyst S3 includes 54.5% MgO, 30% Al2O3, 12.5% CeO2, 2.0% MnO2With 1.0% CuO.
Embodiment 4
The present embodiment provides a kind of preparation methods of regeneration fume from catalytic cracking desulphurization catalyst comprising following steps:
Step 1, aluminum-spinel (MgAl2O4) preparation:
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 44.5g of O, 114.0g2CO3, stirred in 70 DEG C Uniformly, the H containing 1500g is added thereto2Mg (the NO of O, 126.5g3)2·6H2Al (the NO of O, 93.5g3)3·9H2O's is molten Liquid, time for adding 0.5h continue to stir into core crystallization 18h after dripping, and then, cooling, suction filtration is washed to neutrality and dried It is dry, obtain magnesium aluminate spinel A4.
Step 2, the preparation of manganese magnesia-alumina hydrotalcite (MnMgAl-LDH):
The H of 2500g is added in 5 liters of three-necked flask2The Na of the NaOH and 53.0g of O, 126.0g2CO3, stirred in 75 DEG C Uniformly, the H containing 1500g is added thereto2Mn (the NO of O, 5.0g3)2·4H2Mg (the NO of O, 301.8g3)2·6H2O, Al (the NO of 123.5g3)3·9H2The solution of O, time for adding 1.0h continue to stir into core crystallization 20h after dripping, then, Cooling, suction filtration is washed to neutrality simultaneously, obtains manganese magnesia-alumina hydrotalcite B4.
Step 3, the acquisition of regeneration fume from catalytic cracking desulphurization catalyst:
By the Ce (NO of manganese the magnesia-alumina hydrotalcite B3,35.0g of the magnesium aluminate spinel A4,32.0g of 64.2g3)·6H2O, Cu (the NO of 16.0g3)2·6H2The boehmite of O and 115.0g is added to after mixing to be added in turntable bowling machine, is used Sprayer sprays into dilute hydrochloric acid solution to turntable bowling machine.Pass through the continuous spray of the continuous rolling of bowling machine and 18% dilute hydrochloric acid Entering, material is gradually grown up balling-up in pot, and it is 10 hours dry at 150 DEG C by screening selection 1.5-2.5mm partial size bead, It is roasted 12 hours at 750 DEG C, obtains purpose product regeneration fume from catalytic cracking desulphurization catalyst, which is named as S4.It is in terms of 100% by metal oxide mass content, desulphurization catalyst S4 includes 25.5% MgO, 53.5% Al2O3、 14.5% CeO2, 5.0% MnO2With 1.5% CuO.
The physical property of 5 desulphurization catalyst of embodiment is tested
The test that physical property is carried out to the regeneration fume from catalytic cracking desulphurization catalyst of above-described embodiment 1-4 preparation, is surveyed Test result is as shown in table 1.
Table 1
Desulphurization catalyst granularity prepared by the present invention is 1-2.5mm, intensity 30.4- it can be seen from 1 experimental data of table 40.5N/, specific surface area 65.9-82.4m2/kg。
The SO of 6 desulphurization catalyst of embodimentXRemoval performance and reducing/regenerating henchnmrk test
SO is carried out to the regeneration fume from catalytic cracking desulphurization catalyst of above-described embodiment 1-4 preparationXRemoval performance and reduction Regenerability evaluation experimental.Catalyst desulfurizing reaction is carried out using miniature quartz reactor, is 650 DEG C, simulates in reaction temperature Flue gas volume air speed is 1000h-1, catalyst regeneration temperature is 650 DEG C, regeneration gas hydrogen volume air speed 1000h-1Under the conditions of comment The SOx removal performance and reducing/regenerating performance of valence desulphurization catalyst.
Flue gas is by SO2、N2And O2The mixed gas being made by a certain percentage.Wherein SO2For 2000mg/m3, O2It is 3.5 (v) %, remaining is N2。SO2The H generated with micro-coulometric determination, regenerative process2S is analyzed with chromatography.
The desulphurization catalyst for weighing 1.0g is packed into the quartz tube reactor of 8 × 1mm of Φ, is heated under stream of nitrogen gas 650 DEG C, then stop nitrogen, be passed through sulfur dioxide mixture gas 60 minutes, gas flow 17mL/min collects gas, this mistake Journey is the stage of reaction.The gas analysis SO being collected into2Concentration.After reaction, stop sulfur dioxide mixture gas, lead to nitrogen purging 10 minutes, pure hydrogen is passed through 60 minutes at a temperature of 650 DEG C, and hydrogen flowing quantity 17mL/min collects gas, this stage is regeneration Stage.The gas analysis H being collected into2S concentration.
Desulphurization catalyst SOx removal performance SO in reaction mixture gas body2React the change rate of concentration of front and back to indicate, also Former regenerability is indicated with the ratio of the adsorbed sulphur of desulphurization catalyst in the sulphur and reaction adsorption process for generating hydrogen sulfide.
Desulphurization catalyst SOx removal performance takes following formula to calculate:
In formula: DeSOx is the SOx removal efficiency (%) of desulphurization catalyst;C1For SO in gas after reaction2Content (mg/ m3);C2To react SO in preceding gaseous mixture2Content (mg/m3)。
Desulphurization catalyst reducing/regenerating performance takes following formula to calculate:
In formula: K is the regeneration efficiency % of desulphurization catalyst);N is H in regeneration gas2S sulfur content (mg);W1To react Reaction gas total sulfur content (mg) in journey;W2For the total sulfur content (mg) in gas after reaction.
Table 2 is the SOx removal performance and reducing/regenerating Evaluation results of inventive desulfurization catalyst.
Table 2
Desulphurization catalyst Catalyst SOx removal efficiency, % Catalyst regeneration efficiency, %
S1 99.2 100
S2 99.5 100
S3 99.5 100
S4 99.3 100
The regeneration fume from catalytic cracking desulphurization catalyst SO provided by the invention it can be seen from 2 experimental data of tableXDetachability Can be excellent with reducing/regenerating, desulfurization degree is up to 99.5%, and regeneration efficiency reaches 100%.
Embodiment described above is merely to illustrate technical idea and feature of the invention, in the art its object is to make Technical staff it will be appreciated that the contents of the present invention and implement accordingly, patent of the invention only cannot be limited with the present embodiment It encloses, i.e., same changes or modifications made by all disclosed spirit are still fallen in the scope of the patents of the invention.

Claims (10)

1. a kind of preparation method of regeneration fume from catalytic cracking desulphurization catalyst, which is characterized in that method includes the following steps:
The mixed solution that magnesium salts and aluminium salt are prepared is slowly added dropwise in the mixed solution of sodium hydroxide and sodium carbonate preparation step 1 In, it is stirred to react nucleation crystallization after being added dropwise to complete, obtains magnesium aluminate spinel;
The mixed solution that manganese salt, magnesium salts and aluminium salt are prepared is slowly added dropwise and mixes in what sodium hydroxide and sodium carbonate were prepared by step 2 It closes in solution, nucleation crystallization is stirred to react after being added dropwise to complete, obtains manganese magnesia-alumina hydrotalcite;
Magnesium aluminate spinel, manganese magnesia-alumina hydrotalcite, cerous nitrate, copper nitrate and boehmite are uniformly mixed and obtain by step 3 Mixture is continuously sprayed hydrochloric acid solution by mixture during continuous rolling, and sieving obtains small spherical particles;
Step 4 will be roasted to obtain the regeneration fume from catalytic cracking desulphurization catalyst after small spherical particles drying.
2. preparation method according to claim 1, it is characterised in that: in step 1, the mixing of magnesium salts and aluminium salt preparation In solution, in terms of metal oxide, the molar ratio of the magnesium salts and the aluminium salt is (1-5): 1;
Preferably, the magnesium salts includes one of magnesium nitrate, magnesium chloride and magnesium sulfate or a variety of;The aluminium salt includes nitric acid One of aluminium, aluminium chloride and aluminum sulfate are a variety of;
Preferably, in step 1, in the mixed solution that sodium hydroxide and sodium carbonate are prepared, the concentration of the sodium hydroxide is 3- 5mol/L, the concentration of the sodium carbonate are 0.15-0.25mol/L, and the solution of the sodium hydroxide and the sodium carbonate is etc. Volume mixture.
3. preparation method according to claim 1, it is characterised in that: in step 2, what manganese salt, magnesium salts and aluminium salt were prepared In mixed solution, in terms of metal oxide, the molar ratio of the manganese salt, the magnesium salts and the aluminium salt is (0.01-0.2): (1- 4.5): 1;
Preferably, the manganese salt includes manganese nitrate and/or manganese sulfate;The magnesium salts includes magnesium nitrate, magnesium chloride, magnesium sulfate and vinegar One of sour magnesium is a variety of;The aluminium salt includes one of aluminum nitrate, aluminium chloride and aluminum sulfate or a variety of;
Preferably, in step 2, in the mixed solution that sodium hydroxide and sodium carbonate are prepared, the concentration of the sodium hydroxide is 3- 5mol/L, the concentration of the sodium carbonate is 0.1-0.2mol/L, and the solution of the sodium hydroxide and the sodium carbonate is to wait bodies Product mixing.
4. preparation method according to claim 1, which is characterized in that in step 3, by mixture in continuous rolling mistake Hydrochloric acid solution is continuously sprayed in journey, sieving obtains small spherical particles method particularly includes:
Mixture is even added in turntable bowling machine, hydrochloric acid solution is sprayed into turntable bowling machine using sprayer, is passed through The continuous penetrating of the continuous rolling and hydrochloric acid solution of turntable bowling machine makes the material of mixture gradually grow up balling-up, passes through screening Obtain the small spherical particles of 0.2-2.5mm partial size.
5. preparation method according to claim 1 or 4, which is characterized in that the magnesium aluminate spinel, the manganese magnesia-alumina water Talcum, the cerous nitrate, the copper nitrate and the dosage for intending thin water aluminium meet in the desulphurization catalyst being prepared, with gold Belonging to oxide mass content is 100% meter, the Al of MgO, 30%-55% including 25%-50%2O3, 7.5%-15% CeO2, 0.5%-2% MnO2With the CuO of 1%-5%;
Preferably, the concentration of the hydrochloric acid solution is 18%.
6. preparation method according to claim 1 or 2, it is characterised in that: in step 1, dropping temperature is 50-70 DEG C, Time for adding is 0.2-0.5h;
Preferably, control solution ph is 8-10 during being added dropwise;
Preferably, the time being stirred to react after being added dropwise to complete is 4-18h;
Preferably, cooling, suction filtration is further included the steps that after being stirred to react, is washed to neutral and drying;Preferably, drying temperature Degree is 150 DEG C.
7. preparation method according to claim 1 or 3, it is characterised in that: in step 2, dropping temperature is 60-80 DEG C, Time for adding is 0.4-1h;
Preferably, control solution ph is 8-10 during being added dropwise;
Preferably, the time being stirred to react after being added dropwise to complete is 4-20h;
Preferably, cooling, suction filtration is further included the steps that after being stirred to react, is washed to neutral and drying;Preferably, drying temperature Degree is 150 DEG C.
8. preparation method according to claim 1, it is characterised in that: in step 4, the small spherical particles are dried Temperature be 120-150 DEG C, drying time 5-12h;
Preferably, the temperature roasted is 700-850 DEG C, calcining time 3-12h.
9. a kind of regeneration fume from catalytic cracking desulphurization catalyst, it is characterised in that: the desulphurization catalyst is by claim 1-7 Any one preparation method is prepared.
10. desulphurization catalyst according to claim 9, it is characterised in that: with metal oxide mass content for 100% Meter, the desulphurization catalyst includes the Al of MgO, 30%-55% of 25%-50%2O3, 7.5%-15% CeO2, 0.5%- 2% MnO2With the CuO of 1%-5%.
CN201811425042.4A 2018-11-27 2018-11-27 A kind of regeneration fume from catalytic cracking desulphurization catalyst and preparation method thereof Pending CN109453783A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112960684A (en) * 2021-04-07 2021-06-15 长兴谐源化工助剂有限公司 Preparation method of nano calcium hydroxide powder for accelerating flue gas desulfurization
CN113713800A (en) * 2021-09-15 2021-11-30 中国石油化工股份有限公司 High-temperature flue gas desulfurizer and preparation method thereof
CN115845596A (en) * 2022-11-15 2023-03-28 中国石油化工股份有限公司 Catalytic cracking flue gas regenerative dry desulfurization process

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0045170A1 (en) * 1980-07-29 1982-02-03 Katalistiks International, Incorporated A process for combusting sulfur-containing material, a hydrocarbon conversion process including such a combustion process in a catalyst regeneration step and a composition suitable for use as a catalyst in the hydrocarbon conversion process
CN102151484A (en) * 2011-01-27 2011-08-17 山东大学 Catalytic cracking regenerated flue gas sulfur transfer agent and preparation method thereof
CN103480355A (en) * 2012-06-12 2014-01-01 中国石油化工股份有限公司 Organic sulfur hydrolysis catalyst applicable to natural gas large-scale sulfur recovery device and preparation method thereof
CN104548926A (en) * 2015-01-12 2015-04-29 北京三聚环保新材料股份有限公司 Organic sulfur removal process
CN104722311A (en) * 2015-03-12 2015-06-24 张伟 Sulfur-transferring additive for regenerative flue gas in catalytic cracking and preparation method thereof
CN105688648A (en) * 2016-03-23 2016-06-22 中石化炼化工程(集团)股份有限公司 Smoke plume removal agent for FCC flue gas wet desulfurization process as well as preparation method and application of smoke plume removal agent

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0045170A1 (en) * 1980-07-29 1982-02-03 Katalistiks International, Incorporated A process for combusting sulfur-containing material, a hydrocarbon conversion process including such a combustion process in a catalyst regeneration step and a composition suitable for use as a catalyst in the hydrocarbon conversion process
CN102151484A (en) * 2011-01-27 2011-08-17 山东大学 Catalytic cracking regenerated flue gas sulfur transfer agent and preparation method thereof
CN103480355A (en) * 2012-06-12 2014-01-01 中国石油化工股份有限公司 Organic sulfur hydrolysis catalyst applicable to natural gas large-scale sulfur recovery device and preparation method thereof
CN104548926A (en) * 2015-01-12 2015-04-29 北京三聚环保新材料股份有限公司 Organic sulfur removal process
CN104722311A (en) * 2015-03-12 2015-06-24 张伟 Sulfur-transferring additive for regenerative flue gas in catalytic cracking and preparation method thereof
CN105688648A (en) * 2016-03-23 2016-06-22 中石化炼化工程(集团)股份有限公司 Smoke plume removal agent for FCC flue gas wet desulfurization process as well as preparation method and application of smoke plume removal agent

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
贡长生等著: "《现代工业化学》", 30 June 2008, 华中科技大学出版社 *

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112960684A (en) * 2021-04-07 2021-06-15 长兴谐源化工助剂有限公司 Preparation method of nano calcium hydroxide powder for accelerating flue gas desulfurization
CN113713800A (en) * 2021-09-15 2021-11-30 中国石油化工股份有限公司 High-temperature flue gas desulfurizer and preparation method thereof
CN113713800B (en) * 2021-09-15 2024-06-04 中国石油化工股份有限公司 High-temperature flue gas desulfurizing agent and preparation method thereof
CN115845596A (en) * 2022-11-15 2023-03-28 中国石油化工股份有限公司 Catalytic cracking flue gas regenerative dry desulfurization process
CN115845596B (en) * 2022-11-15 2024-05-17 中国石油化工股份有限公司 Catalytic cracking flue gas renewable dry desulfurization process

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Application publication date: 20190312