CN114425439A - A kind of waste catalytic cracking catalyst resurrection method - Google Patents
A kind of waste catalytic cracking catalyst resurrection method Download PDFInfo
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- 239000003054 catalyst Substances 0.000 title claims abstract description 170
- 238000004523 catalytic cracking Methods 0.000 title claims abstract description 105
- 238000000034 method Methods 0.000 title claims abstract description 72
- 239000002699 waste material Substances 0.000 title claims abstract description 21
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000001301 oxygen Substances 0.000 claims abstract description 32
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 32
- 239000001257 hydrogen Substances 0.000 claims abstract description 24
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 24
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 21
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 claims abstract description 21
- 239000012298 atmosphere Substances 0.000 claims abstract description 21
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 65
- 239000000243 solution Substances 0.000 claims description 60
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 40
- 229910052759 nickel Inorganic materials 0.000 claims description 32
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 24
- 229910021529 ammonia Inorganic materials 0.000 claims description 19
- 150000003863 ammonium salts Chemical class 0.000 claims description 15
- 239000007789 gas Substances 0.000 claims description 15
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 12
- 239000007800 oxidant agent Substances 0.000 claims description 11
- 230000001590 oxidative effect Effects 0.000 claims description 11
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 10
- 239000002253 acid Substances 0.000 claims description 9
- 239000003929 acidic solution Substances 0.000 claims description 8
- MNNHAPBLZZVQHP-UHFFFAOYSA-N diammonium hydrogen phosphate Chemical compound [NH4+].[NH4+].OP([O-])([O-])=O MNNHAPBLZZVQHP-UHFFFAOYSA-N 0.000 claims description 6
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 5
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims description 5
- 239000001099 ammonium carbonate Substances 0.000 claims description 5
- 229910052761 rare earth metal Inorganic materials 0.000 claims description 5
- 238000005406 washing Methods 0.000 claims description 5
- 239000004254 Ammonium phosphate Substances 0.000 claims description 4
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 4
- 229910000148 ammonium phosphate Inorganic materials 0.000 claims description 4
- 235000019289 ammonium phosphates Nutrition 0.000 claims description 4
- 150000002910 rare earth metals Chemical class 0.000 claims description 4
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims description 4
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 claims description 3
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 3
- 235000012538 ammonium bicarbonate Nutrition 0.000 claims description 3
- 229910002091 carbon monoxide Inorganic materials 0.000 claims description 3
- 150000002431 hydrogen Chemical class 0.000 claims description 3
- 239000002808 molecular sieve Substances 0.000 claims description 3
- 229910017604 nitric acid Inorganic materials 0.000 claims description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 2
- 235000012501 ammonium carbonate Nutrition 0.000 claims description 2
- 235000019270 ammonium chloride Nutrition 0.000 claims description 2
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 2
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 2
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 claims description 2
- 229910052698 phosphorus Inorganic materials 0.000 claims description 2
- 239000011574 phosphorus Substances 0.000 claims description 2
- 238000012545 processing Methods 0.000 claims description 2
- 238000004064 recycling Methods 0.000 claims description 2
- 239000000377 silicon dioxide Substances 0.000 claims description 2
- 238000011084 recovery Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 23
- 238000010438 heat treatment Methods 0.000 abstract description 6
- 230000008569 process Effects 0.000 description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 16
- 238000001914 filtration Methods 0.000 description 11
- BNIILDVGGAEEIG-UHFFFAOYSA-L disodium hydrogen phosphate Chemical compound [Na+].[Na+].OP([O-])([O-])=O BNIILDVGGAEEIG-UHFFFAOYSA-L 0.000 description 10
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 8
- 230000000052 comparative effect Effects 0.000 description 8
- 238000010992 reflux Methods 0.000 description 8
- 229910052734 helium Inorganic materials 0.000 description 7
- 239000001307 helium Substances 0.000 description 7
- 239000011259 mixed solution Substances 0.000 description 7
- FWABRVJYGBOLEM-UHFFFAOYSA-N diazanium;azane;carbonate Chemical compound N.[NH4+].[NH4+].[O-]C([O-])=O FWABRVJYGBOLEM-UHFFFAOYSA-N 0.000 description 6
- 239000003921 oil Substances 0.000 description 6
- 239000000463 material Substances 0.000 description 5
- 230000009467 reduction Effects 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 4
- 235000011114 ammonium hydroxide Nutrition 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 3
- 238000009833 condensation Methods 0.000 description 3
- 230000005494 condensation Effects 0.000 description 3
- 239000012153 distilled water Substances 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 230000007420 reactivation Effects 0.000 description 3
- 239000012266 salt solution Substances 0.000 description 3
- 229910052720 vanadium Inorganic materials 0.000 description 3
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 238000011109 contamination Methods 0.000 description 2
- 230000009849 deactivation Effects 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 239000008367 deionised water Substances 0.000 description 2
- 229910021641 deionized water Inorganic materials 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000011156 evaluation Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000012452 mother liquor Substances 0.000 description 2
- -1 nickel Chemical class 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- PRKQVKDSMLBJBJ-UHFFFAOYSA-N ammonium carbonate Chemical compound N.N.OC(O)=O PRKQVKDSMLBJBJ-UHFFFAOYSA-N 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 229910052729 chemical element Inorganic materials 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000005660 chlorination reaction Methods 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- SWQJXJOGLNCZEY-UHFFFAOYSA-N helium atom Chemical compound [He] SWQJXJOGLNCZEY-UHFFFAOYSA-N 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052754 neon Inorganic materials 0.000 description 1
- GKAOGPIIYCISHV-UHFFFAOYSA-N neon atom Chemical compound [Ne] GKAOGPIIYCISHV-UHFFFAOYSA-N 0.000 description 1
- 150000002815 nickel Chemical class 0.000 description 1
- 150000002816 nickel compounds Chemical class 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000012299 nitrogen atmosphere Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 238000005486 sulfidation Methods 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 150000003681 vanadium Chemical class 0.000 description 1
- 239000003039 volatile agent Substances 0.000 description 1
- 238000004846 x-ray emission Methods 0.000 description 1
- 238000004876 x-ray fluorescence Methods 0.000 description 1
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J29/00—Catalysts comprising molecular sieves
- B01J29/90—Regeneration or reactivation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/02—Heat treatment
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/04—Gas or vapour treating; Treating by using liquids vaporisable upon contacting spent catalyst
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/04—Gas or vapour treating; Treating by using liquids vaporisable upon contacting spent catalyst
- B01J38/10—Gas or vapour treating; Treating by using liquids vaporisable upon contacting spent catalyst using elemental hydrogen
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/04—Gas or vapour treating; Treating by using liquids vaporisable upon contacting spent catalyst
- B01J38/12—Treating with free oxygen-containing gas
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J38/00—Regeneration or reactivation of catalysts, in general
- B01J38/48—Liquid treating or treating in liquid phase, e.g. dissolved or suspended
- B01J38/64—Liquid treating or treating in liquid phase, e.g. dissolved or suspended using alkaline material; using salts
- B01J38/66—Liquid treating or treating in liquid phase, e.g. dissolved or suspended using alkaline material; using salts using ammonia or derivatives thereof
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G11/00—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils
- C10G11/02—Catalytic cracking, in the absence of hydrogen, of hydrocarbon oils characterised by the catalyst used
- C10G11/04—Oxides
- C10G11/05—Crystalline alumino-silicates, e.g. molecular sieves
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
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- Oil, Petroleum & Natural Gas (AREA)
- Crystallography & Structural Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
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Abstract
Description
技术领域technical field
本发明涉及一种将催化裂化废催化剂进行复活的方法。The present invention relates to a method for reviving the spent catalyst of catalytic cracking.
背景技术Background technique
催化裂化(FCC)催化剂是炼油工艺中应用量最大的一种催化剂,目前我国催化裂化催化剂的使用量近20万吨,其中大约一半随烟气或催化油浆带走而无法回收,每年也会产生约10万吨的废催化裂化催化剂。催化裂化催化剂废剂处理方法包括复活、脱金属处理和建筑材料等,其中最有价值的是复活做催化剂再次使用。Catalytic cracking (FCC) catalyst is the most widely used catalyst in oil refining process. At present, the amount of catalytic cracking catalyst used in my country is nearly 200,000 tons, about half of which is carried away with flue gas or catalytic oil slurry and cannot be recovered. About 100,000 tons of spent catalytic cracking catalyst are produced. Catalytic cracking catalyst waste treatment methods include reactivation, demetallization and building materials, among which the most valuable is reactivation as a catalyst for reuse.
废催化裂化催化剂失活的一种原因是金属污染造成的失活,废催化裂化催化剂的污染金属例如钒、铁和镍。对于污染镍含量较高的废催化剂,催化剂的复活需要进行脱镍处理。然而,研究发现催化裂化废催化剂中的镍结构均相对比较稳定,脱除困难。One cause of deactivation of spent catalytic cracking catalysts is deactivation due to contamination of metals such as vanadium, iron and nickel. For spent catalysts with high contamination nickel content, the reactivation of catalysts requires de-nickel treatment. However, the study found that the nickel structure in the catalytic cracking waste catalyst is relatively stable and difficult to remove.
从废催化剂中脱除镍的方法主要有火法和湿法,其中火法包括硫化法、氯化法,能耗较高,容易产生污染性气体,镍的脱除率也不高。湿法通常为酸法,但研究表明即使酸浓度很高,催化裂化催化剂中的镍脱除十分有限。The methods for removing nickel from spent catalysts mainly include pyrotechnics and wet methods, among which pyrotechnics include sulfidation method and chlorination method, which have high energy consumption, easily generate polluting gas, and the removal rate of nickel is not high. Wet processes are usually acid processes, but studies have shown that nickel removal from catalytic cracking catalysts is very limited even at high acid concentrations.
以上脱镍方法通常以获得镍等金属为主,催化剂的结构往往被破坏,活性难以恢复。The above nickel removal methods are usually mainly to obtain metals such as nickel, the structure of the catalyst is often destroyed, and the activity is difficult to recover.
废催化裂化催化剂脱金属复活方法国外工业常采用的方法为Demet方法,虽然脱金属效率可达70%-80%,但需要密闭空间接替采用三种危险气体,苛刻的处理条件,复杂的处理过程,制约了该技术的推广,同时复活催化剂的稳定性较差。Demetallization and resurrection method of waste catalytic cracking catalyst The method commonly used in foreign industries is the Demet method. Although the demetallization efficiency can reach 70%-80%, it requires a closed space to replace the use of three dangerous gases, harsh treatment conditions, and complex treatment processes. , which restricts the promotion of this technology, and the stability of the resurrection catalyst is poor.
CN100525917C李春义等人采用还原性气氛在高温下将催化裂化催化剂中镍还原为镍,然后进行酸浸脱镍、钒和铁等金属,发现镍脱除率可达70%-80%。但是达到很高的金属脱除时酸强度高,对活性稳定性影响比较大,虽然由于表面酸性的活化单次活性较高,但是循环使用几次后活性下降较快。CN100525917C Li Chunyi and others used reducing atmosphere to reduce nickel in catalytic cracking catalyst to nickel at high temperature, and then carried out acid leaching to remove metals such as nickel, vanadium and iron, and found that the removal rate of nickel could reach 70%-80%. However, when the metal removal reaches a high level, the acid strength is high, which has a great influence on the activity stability. Although the single-shot activity due to the activation of the surface acidity is high, the activity decreases rapidly after several cycles of use.
发明内容:Invention content:
本发明要解决的技术问题是提供一种废催化裂化催化剂的复活方法。The technical problem to be solved by the present invention is to provide a method for reviving the spent catalytic cracking catalyst.
本发明的发明人研究发现,国内原油镍含量比较高,加工国内原料油的废催化裂化催化剂一般镍含量偏高,镍含量高容易使催化剂的氢气选择性偏高,高镍含量本身对分子筛结构破坏不大,有复活空间,但简单地脱镍并不能达到令人满意的复活效果。The inventors of the present invention have found that the nickel content of domestic crude oil is relatively high, and the spent catalytic cracking catalyst for processing domestic raw oil is generally high in nickel content. The damage is not large, and there is room for resurrection, but simply de-nicking cannot achieve a satisfactory resurrection effect.
本发明提供一种废催化裂化催化剂的复活方法,包括:The present invention provides a kind of revival method of spent catalytic cracking catalyst, comprising:
(1)将废催化裂化催化剂(以下也简称废催化剂)在还原气氛中于600-880℃进行处理;(1) Treat the spent catalytic cracking catalyst (hereinafter also referred to as spent catalyst) at 600-880° C. in a reducing atmosphere;
(2)将经过处理的废催化裂化催化剂在氨-铵溶液中于pH为9.5-11和含氧氧化剂存在下进行第一接触,分离得到第一接触后的废催化裂化催化剂(简称第一接触后的废催化剂),任选洗涤;所述氨-铵溶液为含有NH3和NH4 +的溶液,氨-铵溶液的铵和氨的总浓度为4-10mol/L,所述第一接触可以在常压下进行;(2) first contact is carried out with the treated waste catalytic cracking catalyst in ammonia-ammonium solution at pH 9.5-11 and in the presence of oxygen-containing oxidant, and the spent catalytic cracking catalyst (referred to as the first contact for short) after the first contact is obtained by separation The spent catalyst after the catalyst), optionally washed; the ammonia-ammonium solution is a solution containing NH 3 and NH 4 + , and the total concentration of ammonium and ammonia in the ammonia-ammonium solution is 4-10 mol/L, and the first contact It can be carried out under normal pressure;
(3)将步骤(2)的产物进行热处理,所述的热处理例如干燥和/或焙烧。(3) subjecting the product of step (2) to heat treatment, such as drying and/or calcination.
本发明提供的废催化裂化催化剂的复活方法,复活后的废催化裂化催化剂结晶度保留度高,微活指数提高,活性稳定性更高,并能够明显降低氢气产率和/或焦炭产率。本发明提供的废催化裂化催化剂复活方法,氨和铵盐可以回收及循环利用,绿色环保。优选的情况下,可以使废催化裂化催化剂的金属镍脱除率在80%以上情况下,分子筛结构不受到破坏,微活指数提高。The method for reviving the spent catalytic cracking catalyst provided by the invention has high crystallinity retention, improved micro-activity index, higher activity stability, and can significantly reduce hydrogen yield and/or coke yield. In the method for reviving the spent catalytic cracking catalyst provided by the invention, ammonia and ammonium salts can be recovered and recycled, which is green and environmentally friendly. In a preferred case, when the removal rate of metallic nickel of the spent catalytic cracking catalyst is more than 80%, the molecular sieve structure is not damaged, and the micro-activity index is improved.
具体实施方式:Detailed ways:
本发明提供的废催化裂化催化剂复活方法,一种实施方式,所述废催化裂化催化剂的二氧化硅质量分数为30-75质量%,三氧化二铝质量分数为20-65质量%,稀土金属质量分数为0-5质量%,镍质量分数>0.4质量%,例如为0.4-1.5重量%。优选的,所述废催化裂化催化剂的结晶度≥10%例如≥15%。所述结晶度可以参考SH/T 0340-1992 NaY分子筛结晶度测定法方法分析。优选的,废催化裂化催化剂中钒和铁的含量之和不高于0.6质量%。一种实施方式,所述废催化裂化催化剂中污染镍含量明显高于污染钒和铁的含量。An embodiment of the method for reviving a spent catalytic cracking catalyst provided by the present invention, the mass fraction of silica of the spent catalytic cracking catalyst is 30-75 mass %, the mass fraction of aluminum oxide is 20-65 mass %, and the rare earth metal The mass fraction is 0-5 mass %, and the nickel mass fraction is >0.4 mass %, for example, 0.4-1.5 wt %. Preferably, the crystallinity of the spent catalytic cracking catalyst is ≥10%, such as ≥15%. The crystallinity can be analyzed with reference to SH/T 0340-1992 NaY molecular sieve crystallinity determination method. Preferably, the sum of the content of vanadium and iron in the spent catalytic cracking catalyst is not higher than 0.6% by mass. In one embodiment, the content of contaminated nickel in the spent catalytic cracking catalyst is significantly higher than the content of contaminated vanadium and iron.
本发明提供的废催化裂化催化剂复活方法,使废催化裂化催化剂在还原气氛中进行还原。所述还原气氛中含有可以使镍还原的气体,例如含有氢气、CO、烃类物质中的一种或多种,但不限于上述气体。所述还原气氛中还原性气体的浓度为5体积%-100体积%。一种实施方式,所述还原性气氛为氢气、一氧化碳、炼厂干气气氛或为含有上述气体一种或多种以及任选的惰性气体的混合气体的气氛,所述惰性气体例如氮气、氦气、氖气中的一种或多种。The method for reviving the spent catalytic cracking catalyst provided by the invention enables the spent catalytic cracking catalyst to be reduced in a reducing atmosphere. The reducing atmosphere contains a gas that can reduce nickel, for example, contains one or more of hydrogen, CO, and hydrocarbons, but is not limited to the above-mentioned gases. The concentration of the reducing gas in the reducing atmosphere is 5% to 100% by volume. In one embodiment, the reducing atmosphere is hydrogen, carbon monoxide, refinery dry gas atmosphere, or an atmosphere containing a mixture of one or more of the above gases and optionally an inert gas, such as nitrogen, helium One or more of gas and neon gas.
根据本发明提供的废催化裂化催化剂复活方法,于一实施方式,废催化裂化催化剂在还原气氛中进行还原,还原温度为600-880℃,优选650℃-850℃。还原时间例如为0.5-20小时。According to the method for reviving the spent catalytic cracking catalyst provided by the present invention, in one embodiment, the spent catalytic cracking catalyst is reduced in a reducing atmosphere, and the reduction temperature is 600-880°C, preferably 650-850°C. The reduction time is, for example, 0.5-20 hours.
本发明提供的废催化裂化催化剂复活方法,废催化裂化催化剂的还原,可以以固定床方式,也可以流态化方式进行,且不限于此。优选,废催化裂化催化剂的还原采用流态化方式进行,该方式还原快速均匀,便于物料的装入和卸出。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the reduction of the spent catalytic cracking catalyst can be performed in a fixed bed mode or a fluidized mode, and is not limited thereto. Preferably, the reduction of the spent catalytic cracking catalyst is carried out in a fluidized manner, which is fast and uniform, and facilitates the loading and unloading of materials.
本发明提供的废催化裂化催化剂复活方法,所述氨-铵溶液为含氨与铵盐的混合液,其含有NH3和NH4 +。所述铵盐可以是碳酸铵和碳酸氢铵的一种或几种。所述氨-铵溶液中NH3和NH4 +的总浓度(称总氨浓度)为4-10mol/L。所述氨-铵溶液可以通过在混合容器中加入氨水和铵盐或铵盐溶液得到。一种实施方式,加入的NH3与NH4 +的摩尔比为2:1-1:4。第一接触全过程中,所述含氨与铵盐的混合液的pH值保持在9.5-11之间。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the ammonia-ammonium solution is a mixed solution containing ammonia and ammonium salt, and contains NH 3 and NH 4 + . The ammonium salt can be one or more of ammonium carbonate and ammonium bicarbonate. The total concentration of NH 3 and NH 4 + in the ammonia-ammonium solution (called total ammonia concentration) is 4-10 mol/L. The ammonia-ammonium solution can be obtained by adding ammonia water and an ammonium salt or ammonium salt solution in a mixing vessel. In one embodiment, the molar ratio of NH 3 to NH 4 + added is 2:1-1:4. During the whole process of the first contact, the pH value of the mixed solution containing ammonia and ammonium salt is maintained between 9.5-11.
为了使第一接触过程中总氨浓度为4-10mol/L,可以通过加入氨水、通入氨气、加入铵盐或铵盐溶液来保持总氨浓度,由于氨挥发,可以通过冷凝回收,或吸收方法回收挥发的氨气,循环使用,这为本领域技术人员所熟知。一种调节总氨浓度保持恒定的方法例如为氨的冷凝回流。In order to make the total ammonia concentration 4-10 mol/L in the first contact process, the total ammonia concentration can be maintained by adding ammonia water, feeding ammonia gas, adding ammonium salt or ammonium salt solution, and can be recovered by condensation due to the volatilization of ammonia, or The absorption method recovers the volatilized ammonia gas for recycling, which is well known to those skilled in the art. One way to adjust the total ammonia concentration to remain constant is, for example, condensation reflux of ammonia.
本发明提供的废催化裂化催化剂复活方法,所述第一接触的pH值为9.5-11。为了使第一接触全过程中氨与铵盐的混合液溶液的pH值在9.5-11之间,可以将废催化裂化催化剂加入到pH值为9.5-11的氨-铵溶液中,形成第一接触混合液,通过加入氨水或酸调整第一接触混合液的pH值为9.5-11。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the pH value of the first contact is 9.5-11. In order to make the pH value of the mixed solution of ammonia and ammonium salt between 9.5-11 in the whole process of the first contact, the spent catalytic cracking catalyst can be added to the ammonia-ammonium solution with a pH value of 9.5-11 to form the first The pH value of the first contacting mixed solution is adjusted to 9.5-11 by adding ammonia water or acid to the contacting mixed solution.
本发明提供的废催化裂化催化剂复活方法,优选的,氨-铵溶液中废催化裂化催化剂的加入量即氨-铵溶液中废催化裂化催化剂的含量为20-70g/L氨-铵溶液。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, preferably, the amount of the spent catalytic cracking catalyst added in the ammonia-ammonium solution, that is, the content of the spent catalytic cracking catalyst in the ammonia-ammonium solution, is 20-70 g/L ammonia-ammonium solution.
本发明提供的废催化裂化催化剂复活方法,所述的含氧氧化剂为氧气或非气体的含氧氧化剂。一种实施方式,第一接触过程中在氨-铵溶液中通入含有氧气的气体,例如氧气和/或空气和/或其它含氧气的气体。氧气的通入速率可以为0.05-0.3L/(min·g废催化剂)。)。另外一种实施方式,第一接触过程中在氨-铵溶液加入含氧的氧化剂例如H2O2、K2MnO4中的一种或多种。本发明中,所述的氧气和其它气体的体积为标准状况下的体积。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the oxygen-containing oxidant is oxygen or a non-gas oxygen-containing oxidant. In one embodiment, a gas containing oxygen, such as oxygen and/or air and/or other gas containing oxygen, is passed into the ammonia-ammonium solution during the first contacting process. The introduction rate of oxygen can be 0.05-0.3 L/(min·g spent catalyst). ). In another embodiment, during the first contacting process, an oxygen-containing oxidant such as one or more of H 2 O 2 and K 2 MnO 4 is added to the ammonia-ammonium solution. In the present invention, the volume of oxygen and other gases is the volume under standard conditions.
本发明提供的废催化裂化催化剂复活方法,优选情况下,第一接触过程中,氧气的溶解量或所述含氧氧化剂的产氧速率使接触溶液中的氧的浓度不低于0.005g/L(H20)。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, preferably, in the first contact process, the dissolved amount of oxygen or the oxygen production rate of the oxygen-containing oxidant makes the oxygen concentration in the contact solution not less than 0.005g/L (H 2 0).
本发明提供的废催化裂化催化剂复活方法,一种实施方式,第一接触的接触温度为10-100℃,优选10-70℃或25-70℃或25-60℃。第一接触的接触时间可以为10min-120min。所述第一接触的压力没有特殊要求,可以在常压下进行。In an embodiment of the method for reviving a spent catalytic cracking catalyst provided by the present invention, the contact temperature of the first contact is 10-100°C, preferably 10-70°C or 25-70°C or 25-60°C. The contact time of the first contact may be 10min-120min. There is no special requirement for the pressure of the first contact, and it can be carried out under normal pressure.
本发明提供的废催化裂化催化剂复活方法,将经过还原的废催化裂化催化剂于氨-铵溶液中在含氧氧化剂的存在下进行第一接触,然后分离例如过滤,得到第一接触后的废催化裂化催化剂和含氨和铵的母液。所述母液可以回收氨、铵盐以及含镍物质。氨和铵盐可以循环使用,含镍物质可以制备镍或镍化合物。第一接触后的废催化裂化催化剂可以洗涤以洗去其中的氨-铵溶液和含镍物质;所述洗涤例如用水洗涤。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the reduced spent catalytic cracking catalyst is first contacted in an ammonia-ammonium solution in the presence of an oxygen-containing oxidant, and then separated, such as by filtration, to obtain the spent catalytic cracking catalyst after the first contact. Cracking catalyst and mother liquor containing ammonia and ammonium. The mother liquor can recover ammonia, ammonium salts and nickel-containing substances. Ammonia and ammonium salts can be recycled, and nickel-containing substances can be used to prepare nickel or nickel compounds. The spent catalytic cracking catalyst after the first contact may be washed to remove ammonia-ammonium solution and nickel-containing species; such washing, for example, with water.
本发明提供的废催化裂化催化剂复活方法,步骤(2)中第一接触后的废催化裂化催化剂进行洗涤或不洗涤,然后用处理溶液进行处理,所述处理溶液为含磷溶液、含稀土盐的溶液、弱酸性溶液的一种或多种。所述处理,通常包括将洗涤或未洗涤的第一接触后的废催化裂化催化剂与处理溶液混合进行第二接触,在处理温度下搅拌一段时间称为处理时间,然后过滤。处理温度例如为70-100℃例如75-95℃,处理时间优选为10-60min。处理液与第一接触后的废催化裂化催化剂的重量比例如为2-15:1或4-10:1。优选的,洗涤后的第一接触后的废催化裂化催化剂用稀土盐溶液和/或弱酸性溶液进行处理以使增强催化剂活性。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, the spent catalytic cracking catalyst after the first contact in step (2) is washed or not washed, and then treated with a treatment solution, wherein the treatment solution is a phosphorus-containing solution, a rare-earth salt-containing solution One or more of the solution and weak acid solution. The treatment generally involves mixing the washed or unwashed spent catalytic cracking catalyst after the first contact with the treatment solution for a second contact, stirring at the treatment temperature for a period of time called treatment time, and then filtering. The treatment temperature is, for example, 70-100° C., such as 75-95° C., and the treatment time is preferably 10-60 min. The weight ratio of the treatment liquid to the spent catalytic cracking catalyst after the first contact is, for example, 2-15:1 or 4-10:1. Preferably, the washed first contacted spent catalytic cracking catalyst is treated with a rare earth salt solution and/or a weakly acidic solution to enhance catalyst activity.
本发明提供的废催化裂化催化剂复活方法,一种优选的实施方式,所述的处理溶液为弱酸性溶液,该方法包括:将第一接触后的废催化裂化催化剂洗涤或不洗涤,然后与弱酸性溶液进行第二接触,第二接触的接触温度为70-100℃例如75-95℃,第二接触的接触时间优选为10-60min;所述弱酸性溶液为含有盐酸、磷酸、硝酸、硫酸、硫酸铵、氯化铵、磷酸铵、磷酸氢铵中的一种或几种的溶液,所述弱酸性溶液的pH值为3.5-5。In a preferred embodiment of the method for reviving spent catalytic cracking catalyst provided by the present invention, the treatment solution is a weakly acidic solution, and the method comprises: washing or not washing the spent catalytic cracking catalyst after the first contact, and then mixing the spent catalytic cracking catalyst with weak acid solution. The acidic solution is subjected to the second contact, the contact temperature of the second contact is 70-100 ° C, such as 75-95 ° C, and the contact time of the second contact is preferably 10-60 min; the weakly acidic solution contains hydrochloric acid, phosphoric acid, nitric acid, sulfuric acid. , one or more solutions of ammonium sulfate, ammonium chloride, ammonium phosphate and ammonium hydrogen phosphate, the pH value of the weakly acidic solution is 3.5-5.
本发明提供的废催化裂化催化剂复活方法,步骤(3)中,对步骤(2)得到的产物进行热处理,热处理的温度优选为100-550℃,所述热处理例如干燥和/或焙烧。In the method for reviving the spent catalytic cracking catalyst provided by the present invention, in step (3), the product obtained in step (2) is subjected to heat treatment, and the temperature of the heat treatment is preferably 100-550° C. The heat treatment is, for example, drying and/or roasting.
下面通过具体实施例对本发明做进一步的说明,本实施例中所用的废催化裂化催化剂,其基本化学组成如表1所示,化学组成采用X射线荧光法(XRF)测定。参照ASTM D7085-04(2010)流化催化裂化催化剂中化学元素测定标准指南—X射线荧光光谱法测定指南。采用NB/SH/T 0952-2017测定催化剂微反活性。。采用SH/T 0340-1992NaY分子筛结晶度测定法对催化剂的结晶度进行测试。采用ASTMD7964/D7964M-14ACE评价方法进行ACE测试,采用武混三原料油进行评价试验,20℃密度0.9044g/cm3,初馏点243℃,70%馏出温度473℃。H2/CH4为氢气指数。The present invention will be further described below through specific examples. The basic chemical composition of the spent catalytic cracking catalyst used in this example is shown in Table 1, and the chemical composition is determined by X-ray fluorescence (XRF). Refer to ASTM D7085-04 (2010) Standard Guide for the Determination of Chemical Elements in Fluidized Catalytic Cracking Catalysts—Guide to the Determination of X-ray Fluorescence Spectrometry. The catalyst microreactivity was determined by NB/SH/T 0952-2017. . The crystallinity of the catalyst was tested by SH/T 0340-1992NaY molecular sieve crystallinity determination method. The ACE test was carried out by ASTMD7964/D7964M-14ACE evaluation method, and the evaluation test was carried out using Wuxian three raw material oil. The density at 20°C was 0.9044g/cm3, the initial boiling point was 243°C, and the 70% distillation temperature was 473°C. H 2 /CH 4 is the hydrogen index.
表1Table 1
实施例1Example 1
称取10克废催化裂化催化剂C1在800℃下氢气含量30体积%的氢-氦气氛中流态化焙烧3h,得到还原后的废催化裂化催化剂HC1。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L、NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热,并使用冷凝管用自来水(温度16℃)使挥发物质冷却,冷凝物回流(以下也称作使挥发物质冷凝回流)。升温至45℃加入10g还原后的废催化裂化催化剂HC1,以1L/min通氧气30min,进行第一接触。整个第一接触过程的pH为10.1-10.5。过滤后得到第一接触后的废催化裂化催化剂。第一接触后的废催化裂化催化剂与pH为4的磷酸溶液进行第二接触,其中第一接触后的废催化剂与磷酸溶液的重量比为1:5,第二接触的温度为80℃,第二接触的接触时间为30min,过滤后用100ml蒸馏水室温下淋洗,在150℃干燥器中干燥,得到复活催化剂FC1-1。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined in a hydrogen-helium atmosphere with a hydrogen content of 30% by volume at 800° C. for 3 hours to obtain a reduced spent catalytic cracking catalyst HCl. In a 1L three-necked flask, add 200ml of NH 3 and NH 4 + with a total concentration of 8 mol/L, NH 3 : CO 3 2 - being an ammonia-ammonium carbonate solution with a mass ratio of 135:86, turn on the water bath for heating, and use a condenser tube with The volatile matter was cooled by tap water (temperature 16°C), and the condensate was refluxed (hereinafter also referred to as condensation reflux of the volatile matter). The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst HCl was added, and oxygen was passed through at 1 L/min for 30 min to carry out the first contact. The pH throughout the first contacting process was 10.1-10.5. The spent catalytic cracking catalyst after the first contact is obtained after filtration. The spent catalytic cracking catalyst after the first contact is subjected to a second contact with a phosphoric acid solution having a pH of 4, wherein the weight ratio of the spent catalyst after the first contact to the phosphoric acid solution is 1:5, the temperature of the second contact is 80° C. The contact time of the second contact is 30 min, after filtration, rinse with 100 ml of distilled water at room temperature, and dry in a 150° C. desiccator to obtain a resurrection catalyst FC1-1.
复活催化剂FC1-1的镍质量分数为0.23%,结晶度为13.9%,微反活性为65。ACE测试氢气指数为0.32The nickel mass fraction of the resurrection catalyst FC1-1 is 0.23%, the crystallinity is 13.9%, and the microreactivity is 65. ACE test hydrogen index of 0.32
将复活后的催化剂反应再生循环三次(每次的反应温度550℃,进油量1.5g(剂油比为6),反应时间75秒,再生温度为700℃,下同),再次测定微反活性为63。The revived catalyst was regenerated and regenerated three times (the reaction temperature of each time was 550 ° C, the oil input was 1.5 g (the ratio of agent to oil was 6), the reaction time was 75 seconds, and the regeneration temperature was 700 ° C, the same below), and the micro-reaction was measured again. The activity is 63.
实施例2Example 2
称取10克废催化裂化催化剂C1在800℃下氢气含量30体积%的氢-氦气氛下流态化焙烧3h,得到还原后的废催化裂化催化剂HC2。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L,NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂HC2,以1L/min通氧气30min,进行第一接触。整个第一接触过程的pH值为10.1-10.5。过滤后用100ml蒸馏水室温下淋洗两遍后,得到第一接触后的废催化裂化催化剂。在150℃干燥器中干燥,得到复活催化剂FC1-2。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined in a fluidized state at 800° C. under a hydrogen-helium atmosphere with a hydrogen content of 30% by volume for 3 hours to obtain a reduced spent catalytic cracking catalyst HC2. In a 1L three-necked flask, add 200ml of NH 3 and NH 4 + the total concentration of 8mol/L, NH 3 : CO 3 2 - is an ammonia-ammonium carbonate solution with a mass ratio of 135:86, turn on the water bath to heat and use a condenser to make Volatile material condenses to reflux. The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst HC2 was added, and oxygen was passed through at 1 L/min for 30 min to carry out the first contact. The pH value of the whole first contacting process is 10.1-10.5. After filtration, the spent catalytic cracking catalyst after the first contact was obtained after being rinsed twice with 100 ml of distilled water at room temperature. It was dried in a desiccator at 150°C to obtain a resurrected catalyst FC1-2.
复活催化剂FC1-2的镍质量分数为0.26%,结晶度为14.1%,微反活性为62。ACE测试氢气指数为0.37The nickel mass fraction of the resurrection catalyst FC1-2 is 0.26%, the crystallinity is 14.1%, and the microreactive activity is 62. ACE test hydrogen index of 0.37
将复活后的催化剂反应再生循环三次,再次测定微反活性为59。The revived catalyst was regenerated and regenerated three times, and the microreaction activity was determined to be 59 again.
实施例3Example 3
称取10克废催化裂化催化剂C1在750℃下一氧化碳含量60%的一氧化碳-N2气氛下固定床方式焙烧6h,得到还原后的废催化裂化催化剂HC3。在1L的三口烧瓶中加入200mlNH3和碳酸氢铵的混合溶液,混合溶液的氨和铵总浓度为10mol/L,NH3:CO3 2-为100:65质量比的氨-碳酸氢铵溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至40℃加入还原焙烧后的废催化剂10g以1.5L/min通氧气20min进行第一接触。整个第一接触过程的pH值为9.8-10.3,过滤得到第一接触后的废催化裂化催化剂,进行水洗(用温度为60℃的去离子水淋洗,水与第一接触后的废催化裂化催化剂的重量比为10:1);水洗后的第一接触后的废催化裂化催化剂用pH为4的磷酸铵溶液处理,其中第一接触后的废催化剂与磷酸铵溶液的重量比为1:8,处理温度为80℃,处理时间为50min,过滤,在120℃干燥器中干燥,得到复活催化剂FC1-3。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined at 750°C in a carbon monoxide-N2 atmosphere with a carbon monoxide content of 60% for 6 hours in a fixed bed manner to obtain a reduced spent catalytic cracking catalyst HC3. In a 1L three-necked flask, add 200ml of NH 3 and a mixed solution of ammonium bicarbonate, the ammonia and ammonium total concentration of the mixed solution is 10mol/L, and NH 3 : CO 3 2 - is an ammonia-ammonium bicarbonate solution with a mass ratio of 100:65 , turn on the water bath to heat and use the condenser tube to condense the volatiles to reflux. The temperature was raised to 40° C. and 10 g of the spent catalyst after reduction and roasting was added to conduct the first contact with oxygen at 1.5 L/min for 20 min. The pH value of the whole first contact process is 9.8-10.3, and the spent catalytic cracking catalyst after the first contact is obtained by filtration, and washed with water (with deionized water at a temperature of 60 ℃, water and the spent catalytic cracking catalyst after the first contact) The weight ratio of the catalyst is 10:1); the spent catalytic cracking catalyst after the first contact after washing is treated with an ammonium phosphate solution with pH of 4, wherein the weight ratio of the spent catalyst after the first contact and the ammonium phosphate solution is 1: 8. The treatment temperature is 80°C, the treatment time is 50min, filtered, and dried in a 120°C desiccator to obtain the resurrection catalyst FC1-3.
复活催化剂FC1-3的镍质量分数为0.23%,结晶度为13.7%,微反活性为65。ACE测试氢气指数为0.34。The nickel mass fraction of the resurrection catalyst FC1-3 was 0.23%, the crystallinity was 13.7%, and the microreactivity was 65. The ACE test hydrogen index is 0.34.
将复活后的催化剂反应再生循环三次,再次测定微反活性为64。The revived catalyst was regenerated and regenerated three times, and the microreactivity was determined to be 64 again.
对比例1Comparative Example 1
在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L,NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂C1,以1L/min通氧气30min。整个第一接触过程的pH为10.1-10.5。过滤后得到第一接触后的废催化裂化催化剂。接触后的废催化裂化催化剂采用pH为4的磷酸溶液处理,其中第一接触后的废催化剂与磷酸溶液的重量比为1:5,处理温度为80℃,处理时间为30min,过滤后采用100ml的蒸馏水进行室温下淋洗,在150℃干燥器中干燥,得到复活催化剂FC1-4。In a 1L three-necked flask, add 200ml of NH 3 and NH 4 + the total concentration of 8mol/L, NH 3 : CO 3 2 - is an ammonia-ammonium carbonate solution with a mass ratio of 135:86, turn on the water bath to heat and use a condenser to make Volatile material condenses to reflux. The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst C1 was added, and oxygen was passed through at 1 L/min for 30 min. The pH throughout the first contacting process was 10.1-10.5. The spent catalytic cracking catalyst after the first contact is obtained after filtration. The spent catalytic cracking catalyst after the contact is treated with a phosphoric acid solution with a pH of 4, wherein the weight ratio of the spent catalyst after the first contact to the phosphoric acid solution is 1:5, the treatment temperature is 80 ° C, the treatment time is 30 min, and 100 ml of The distilled water was rinsed at room temperature and dried in a desiccator at 150 °C to obtain a resurrected catalyst FC1-4.
复活催化剂FC1-4的镍质量分数为0.88%,结晶度为14.0%,微反活性为62。ACE测试氢气指数为0.83。The nickel mass fraction of the resurrection catalyst FC1-4 is 0.88%, the crystallinity is 14.0%, and the micro-reactivity is 62. The ACE test hydrogen index is 0.83.
将复活后的催化剂反应再生循环三次,再次测定微反活性为56。The revived catalyst was regenerated and regenerated three times, and the microreaction activity was determined to be 56 again.
对比例2Comparative Example 2
称取10克废催化裂化催化剂C1在500℃下氢气含量30体积%的氢-氦气氛下流态化焙烧3h,得到还原后的废催化裂化催化剂HC5。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L,NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂HC5,以1L/min通氧气30min。整个接触过程的pH为10.1-10.5。过滤后得到接触后的废催化裂化催化剂。接触后的废催化裂化催化剂采用pH为4的磷酸溶液进行第二处理,其中第一接触后的废催化剂与磷酸溶液的重量比为1:5,处理温度为80℃,处理时间为30min,过滤,在150℃干燥器中干燥,得到复活催化剂FC1-5。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined for 3 hours in a hydrogen-helium atmosphere with a hydrogen content of 30% by volume at 500° C. to obtain a reduced spent catalytic cracking catalyst HC5. In a 1L three-necked flask, add 200ml of NH 3 and NH 4 + the total concentration of 8mol/L, NH 3 : CO 3 2 - is an ammonia-ammonium carbonate solution with a mass ratio of 135:86, turn on the water bath to heat and use a condenser to make Volatile material condenses to reflux. The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst HC5 was added, and oxygen was passed through at 1 L/min for 30 min. The pH throughout the contact process was 10.1-10.5. After filtration, the contacted spent catalytic cracking catalyst is obtained. The spent catalytic cracking catalyst after the contact is treated with a phosphoric acid solution with a pH of 4 for the second treatment, wherein the weight ratio of the spent catalyst after the first contact to the phosphoric acid solution is 1:5, the treatment temperature is 80° C., and the treatment time is 30min. Filter , and dried in a desiccator at 150 °C to obtain a resurrection catalyst FC1-5.
复活催化剂FC1-5的镍质量分数为0.82%,结晶度为13.9%,微反活性为61。ACE测试氢气指数为0.79。The nickel mass fraction of the resurrection catalyst FC1-5 was 0.82%, the crystallinity was 13.9%, and the microreactivity was 61. The ACE test hydrogen index is 0.79.
将复活后的催化剂反应再生循环三次,再次测定微反活性为54。The revived catalyst was regenerated and regenerated three times, and the microreactivity was determined to be 54 again.
对比例3Comparative Example 3
称取10克废催化裂化催化剂C1在800℃下氢气含量30体积%的氢-氦气氛下流态化焙烧3h,得到还原后的废催化裂化催化剂HC6。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L,NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂HC6,整个接触过程的pH为10.5-11.0。过滤后得到接触后的废催化裂化催化剂。接触后的废催化裂化催化剂采用pH为4的磷酸溶液进行第二接触处理,其中接第一接触后的废催化剂与磷酸溶液的重量比为1:5,处理温度为80℃,处理时间为30min,过滤,在150℃干燥器中干燥,得到复活催化剂FC1-6。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined for 3 hours in a hydrogen-helium atmosphere with a hydrogen content of 30% by volume at 800° C. to obtain a reduced spent catalytic cracking catalyst HC6. In a 1L three-necked flask, add 200ml of NH 3 and NH 4 + with a total concentration of 8mol/L, NH 3 : CO 3 2 - being an ammonia-ammonium carbonate solution with a mass ratio of 135:86, turn on the water bath to heat and use a condenser to make Volatile material condenses to reflux. The temperature was raised to 45° C. and 10 g of the reduced waste catalytic cracking catalyst HC6 was added, and the pH of the entire contact process was 10.5-11.0. After filtration, the contacted spent catalytic cracking catalyst is obtained. The spent catalytic cracking catalyst after the contact is treated with a phosphoric acid solution with a pH of 4 for the second contact treatment, wherein the weight ratio of the spent catalyst after the first contact with the phosphoric acid solution is 1:5, the treatment temperature is 80 ° C, and the treatment time is 30min , filtered, and dried in a desiccator at 150 °C to obtain a resurrected catalyst FC1-6.
复活催化剂FC1-6的镍质量分数为0.59%,结晶度为13.8%,微反活性为62。ACE测试氢气指数为0.68。The nickel mass fraction of the resurrection catalyst FC1-6 is 0.59%, the crystallinity is 13.8%, and the micro-reactivity is 62. The ACE test hydrogen index is 0.68.
将复活后的催化剂反应再生循环三次,再次测定微反活性为55。The revived catalyst was regenerated and regenerated three times, and the microreaction activity was determined to be 55 again.
对比例4Comparative Example 4
称取10克废催化裂化催化剂C1在800℃下氢气氛下焙烧6h。然后在90℃用0.5%的硝酸溶液洗涤3次,每次1h,每次酸溶液与催化剂质量比为4,。酸洗后的催化剂过滤时用去离子水冲洗3次,每次10ml,在120℃干燥器中充分干燥处理,得到复活催化剂FC1-7。10 grams of spent catalytic cracking catalyst C1 were weighed and calcined at 800 °C for 6 h in a hydrogen atmosphere. Then wash with 0.5% nitric acid solution 3 times at 90°C for 1 h each time, each time the mass ratio of acid solution to catalyst is 4,. The acid-washed catalyst was washed with deionized water three times, 10 ml each time, and fully dried in a 120° C. desiccator to obtain a resurrected catalyst FC1-7.
复活催化剂FC1-7的镍质量分数为0.22%,结晶度为11.6%,微反活性为63。ACE测试氢气指数为0.31。The nickel mass fraction of the resurrection catalyst FC1-7 is 0.22%, the crystallinity is 11.6%, and the microreactive activity is 63. The ACE test hydrogen index is 0.31.
将复活后的催化剂反应再生循环三次,再次测定微反活性为50。The revived catalyst was regenerated and regenerated three times, and the microreaction activity was determined to be 50 again.
对比例5Comparative Example 5
称取10克废催化裂化催化剂C1在800℃下氢气含量30体积%的氢-氦气氛下流态化焙烧3h,得到还原后的废催化裂化催化剂HC8。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L的纯氨溶液,打开水浴加热并使用冷凝管使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂HC8,以1L/min通氧气30min。整个接触过程的pH为10.2-11.0。过滤后得到第一接触后的废催化裂化催化剂。第一接触后的废催化裂化催化剂采用pH为4的磷酸溶液进行第二接触处理,其中第一接触后的废催化剂与磷酸溶液的重量比为1:5,处理温度为80℃,处理时间为30min,过滤,在150℃干燥器中干燥,得到复活催化剂FC1-8。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined in a fluidized state at 800° C. under a hydrogen-helium atmosphere with a hydrogen content of 30% by volume for 3 hours to obtain a reduced spent catalytic cracking catalyst HC8. In a 1L three-necked flask, add 200ml of pure ammonia solution with a total concentration of 8mol/L of NH 3 and NH 4 + , turn on the water bath to heat and use a condenser to condense and reflux volatile substances. The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst HC8 was added, and oxygen was passed through at 1 L/min for 30 min. The pH throughout the contact process was 10.2-11.0. The spent catalytic cracking catalyst after the first contact is obtained after filtration. The spent catalytic cracking catalyst after the first contact is treated with a phosphoric acid solution with a pH of 4 for the second contact treatment, wherein the weight ratio of the spent catalyst after the first contact to the phosphoric acid solution is 1:5, the treatment temperature is 80 ° C, and the treatment time is 30min, filtered and dried in a desiccator at 150°C to obtain a resurrection catalyst FC1-8.
复活催化剂FC1-8的镍质量分数为0.38%,结晶度为12.9%,微反活性为62。ACE测试氢气指数为0.67。The nickel mass fraction of the resurrection catalyst FC1-8 is 0.38%, the crystallinity is 12.9%, and the microreactive activity is 62. The ACE test hydrogen index is 0.67.
将复活后的催化剂反应再生循环三次,再次测定微反活性为54。The revived catalyst was regenerated and regenerated three times, and the microreactivity was determined to be 54 again.
对比例6Comparative Example 6
称取10克废催化裂化催化剂C1在800℃下氢气含量30体积%的氢-氦气氛下流态化焙烧3h,得到还原后的废催化裂化催化剂HC9。在1L的三口烧瓶中加入200ml NH3和NH4 +的总浓度为8mol/L,NH3:CO3 2-为135:86质量比的氨-碳酸铵溶液,打开水浴加热并使挥发物质冷凝回流。升温至45℃加入10g还原后的废催化裂化催化剂HC9,以1L/min通氧气30min。整个第一接触过程的pH为10.1-10.5。过滤后得到第一接触后的废催化裂化催化剂。第一接触后的废催化裂化催化剂采用pH为2的盐酸溶液进行第二接触处理,其中第一接触后的废催化剂与盐酸溶液的重量比为1:5,处理温度为80℃,处理时间为30min,过滤,在150℃干燥器中干燥,得到复活催化剂FC1-9。10 grams of spent catalytic cracking catalyst C1 was weighed and calcined for 3 hours in a hydrogen-helium atmosphere with a hydrogen content of 30% by volume at 800° C. to obtain a reduced spent catalytic cracking catalyst HC9. In a 1L three-necked flask, add 200ml of NH 3 and NH 4 The total concentration of 8mol/L, NH 3 : CO 3 2 - is an ammonia-ammonium carbonate solution with a mass ratio of 135:86, open a water bath to heat and condense the volatile matter backflow. The temperature was raised to 45° C., 10 g of the reduced waste catalytic cracking catalyst HC9 was added, and oxygen was passed through at 1 L/min for 30 min. The pH throughout the first contacting process was 10.1-10.5. The spent catalytic cracking catalyst after the first contact is obtained after filtration. The waste catalytic cracking catalyst after the first contact adopts the hydrochloric acid solution of pH 2 to carry out the second contact treatment, wherein the weight ratio of the waste catalyst after the first contact to the hydrochloric acid solution is 1:5, the treatment temperature is 80 ° C, and the treatment time is 30min, filtered and dried in a desiccator at 150°C to obtain a resurrected catalyst FC1-9.
复活催化剂FC1-9的镍质量分数为0.21%,结晶度为12.5%,微反活性为62。ACE测试氢气指数为0.35。The nickel mass fraction of the resurrection catalyst FC1-9 is 0.21%, the crystallinity is 12.5%, and the microreactive activity is 62. The ACE test hydrogen index is 0.35.
将复活后的催化剂反应再生循环三次,再次测定微反活性为49。The revived catalyst was regenerated and regenerated three times, and the microreactive activity was determined to be 49 again.
实施例1-3和对比例1-6得到的复活催化剂性质列于表2。The properties of the revived catalysts obtained in Examples 1-3 and Comparative Examples 1-6 are listed in Table 2.
表2Table 2
由表2可见,本发明提供的复活方法,可以使镍的脱除率达到70%以上,能够大幅降低镍含量,降低氢气指数。本发明提供的复活方法,可以使催化剂结晶度得到较好保持。本发明方法可以提高复活催化剂稳定性,复活催化剂经过三次反应后的催化剂活性损失较小。对比例方法得到的复活催化剂,虽然活性提高,但是结晶度下降更多,活性稳定性较差。It can be seen from Table 2 that the resurrection method provided by the present invention can make the removal rate of nickel reach more than 70%, can greatly reduce the nickel content, and reduce the hydrogen index. The resurrection method provided by the present invention can better maintain the crystallinity of the catalyst. The method of the invention can improve the stability of the resurrection catalyst, and the catalyst activity loss of the resurrection catalyst after three reactions is small. Although the activity of the resurrected catalyst obtained by the method of the comparative example is improved, the crystallinity decreases more and the activity stability is poor.
以上详细描述了本公开的优选实施方式,但是,本公开并不限于上述实施方式中的具体细节,在本公开的技术构思范围内,可以对本公开的技术方案进行多种简单变型,这些简单变型均属于本公开的保护范围。The preferred embodiments of the present disclosure are described above in detail, however, the present disclosure is not limited to the specific details of the above-mentioned embodiments. Within the scope of the technical idea of the present disclosure, various simple modifications can be made to the technical solutions of the present disclosure. These simple modifications All belong to the protection scope of the present disclosure.
另外需要说明的是,在上述具体实施方式中所描述的各个具体技术特征,在不矛盾的情况下,可以通过任何合适的方式进行组合,为了避免不必要的重复,本公开对各种可能的组合方式不再另行说明。In addition, it should be noted that, the specific technical features described in the above-mentioned specific embodiments can be combined in any suitable manner unless they are inconsistent. In order to avoid unnecessary repetition, the present disclosure provides The combination method will not be specified otherwise.
此外,本公开的各种不同的实施方式之间也可以进行任意组合,只要其不违背本公开的思想,其同样应当视为本公开所公开的内容。In addition, the various embodiments of the present disclosure can also be arbitrarily combined, as long as they do not violate the spirit of the present disclosure, they should also be regarded as the contents disclosed in the present disclosure.
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