CN112547080A - Method for recycling supported hydrogenation catalyst - Google Patents

Method for recycling supported hydrogenation catalyst Download PDF

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CN112547080A
CN112547080A CN202011575839.XA CN202011575839A CN112547080A CN 112547080 A CN112547080 A CN 112547080A CN 202011575839 A CN202011575839 A CN 202011575839A CN 112547080 A CN112547080 A CN 112547080A
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recycling
catalyst
hydrogenation catalyst
waste
carrier
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CN112547080B (en
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路蒙蒙
刘杰
王美玲
原全太
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Sinochem Quanzhou Petrochemical Co Ltd
Sinochem Quanzhou Energy Technology Co Ltd
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Sinochem Quanzhou Petrochemical Co Ltd
Sinochem Quanzhou Energy Technology Co Ltd
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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
    • 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
    • B01J35/61310-100 m2/g
    • 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
    • B01J23/85Chromium, molybdenum or tungsten
    • B01J23/88Molybdenum
    • B01J23/883Molybdenum and nickel
    • 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
    • B01J35/615100-500 m2/g
    • 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
    • B01J35/63Pore volume
    • B01J35/6350.5-1.0 ml/g
    • 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
    • B01J35/64Pore diameter
    • B01J35/6472-50 nm
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J38/00Regeneration or reactivation of catalysts, in general
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING 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
    • C10G45/00Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds
    • C10G45/02Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing
    • C10G45/04Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing characterised by the catalyst used
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING 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
    • C10G45/00Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds
    • C10G45/02Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing
    • C10G45/04Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing characterised by the catalyst used
    • C10G45/06Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing characterised by the catalyst used containing nickel or cobalt metal, or compounds thereof
    • C10G45/08Refining of hydrocarbon oils using hydrogen or hydrogen-generating compounds to eliminate hetero atoms without changing the skeleton of the hydrocarbon involved and without cracking into lower boiling hydrocarbons; Hydrofinishing characterised by the catalyst used containing nickel or cobalt metal, or compounds thereof in combination with chromium, molybdenum, or tungsten metals, or compounds thereof
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/584Recycling of catalysts

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Catalysts (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)

Abstract

The invention discloses a method for recycling a supported hydrogenation catalyst, and belongs to the field of catalyst recycling. The deactivated hydrogenation catalyst is regenerated and sieved, and the sieved small particles and powder are treated as solid garbage, so that the environment is polluted and the resource waste is caused. In the invention, firstly, the screened waste catalyst is crushed to below 50 microns, then the crushed waste catalyst is added into a mixing and kneading process for preparing the carrier according to a certain proportion, the mixed carrier is prepared by extrusion molding, drying and roasting in an inert gas atmosphere, the carbon on the waste catalyst weakens the interaction between metal and the carrier, and the active component impregnation liquid is supplemented for loading, so that the prepared catalyst has higher hydrodesulfurization activity. The method can completely recycle the waste catalyst, and solves the problem of waste of the conventional waste catalyst as solid garbage disposal in one step.

Description

Method for recycling supported hydrogenation catalyst
Technical Field
The invention belongs to the technical field of hydrogenation catalyst recovery, and particularly relates to a method for recycling a supported hydrogenation catalyst.
Background
Hydrogenation catalysts are the most important catalysts in petroleum processing and generally include hydrofinishing, hydrotreating and hydrocracking catalysts. The hydrogenation catalyst for industrial application is a supported hydrogenation catalyst prepared by using a VIB group metal or a VIB group and VIIIB group binary or ternary metal system as an active center, using alumina or a composite oxide obtained by doping alumina and one or more components of other metal oxides (such as titanium oxide, zirconium oxide, silicon oxide, amorphous silicon aluminum, molecular sieves, zeolite and the like) as a carrier and adopting a method of impregnation and the like. The fresh catalyst is sulfurized to generate activity, and can form type I or type II active centers according to different preparation conditions. The dispersion degree of the I-type active center is high, the interaction between the active center and the carrier is strong, the vulcanization is insufficient, and the intrinsic activity of the active center is low; the dispersion degree of the II type active center is low, the action of the active center and the carrier is weak, the sulfuration is complete, and the intrinsic activity is high. Most researchers have been working on the development of highly active type II active site hydrogenation catalysts.
The appropriate weakening of the forces between the support and the active component is one of the methods for the development of highly active hydrogenation catalysts. Generally, the introduction of an amount of carbon on the catalyst isolates the direct interaction of the active metal and the support, promoting the formation of type II active centers. For the regenerated catalyst, considering the damage of high temperature to the catalyst structure, and the migration, agglomeration and loss of active metal, the regeneration temperature is generally not higher than 500 ℃, carbon on the catalyst is not easy to burn off at the temperature, and a certain amount of carbon exists on the regenerated catalyst. After regeneration, the catalyst needs to be sieved to remove fine particles, so that the pressure drop of a reaction system is prevented from being increased due to the fact that the fine particles block a catalyst bed layer or a pipeline, and unplanned shutdown is avoided. The screened fine particles are generally used as industrial waste to be buried, and the treatment mode not only wastes resources, but also causes environmental pollution.
The recycling of the spent catalyst is a constant concern. Some recovery techniques of the spent catalyst have been developed, and most techniques mainly recover metals in the spent catalyst because of high metal recovery value. Chinese patent CN200810228402.1 discloses a method for recovering molybdenum from molybdenum-containing spent catalyst, which comprises roasting and crushing the spent catalyst, mixing with alkaline substance, roasting, leaching with mixed acid solution, and precipitating with alkaline solution to recover molybdenum. CN201110432230.1 discloses a method for recovering metal tungsten and nickel from waste nickel-tungsten catalysts, which comprises the steps of carrying out high-temperature reduction roasting on the waste catalysts, carrying out extraction separation and concentration crystallization on a replacement leached solution to obtain nickel crystals, carrying out high-temperature roasting on the replacement leached filter residues, washing with hot water, and recovering tungsten by using acid. CN202010405370.9 discloses a method for recovering and preparing solid sodium metaaluminate and pseudo-boehmite from molybdenum-nickel spent catalyst. Firstly, extracting, roasting and screening the inactivated hydrogenation demetalization catalyst, then, sequentially carrying out saturated dipping treatment by using an organic acid solution and an alkali solution, and finally, filtering, drying and roasting to recover the carrier component.
The method uses a large amount of acid and alkali no matter the metal components in the waste catalyst or the carrier are recovered, multiple times of extraction is needed, the extraction process is very complicated to control, the recovery rate is low, the product purity is low, and the industrial production difficulty is high. The fine particles screened out in the regeneration process are used as industrial waste to be buried, so that resources are wasted, and environmental pollution is caused. Therefore, it is necessary to develop a method for recycling the waste hydrogenation catalyst with low cost.
Disclosure of Invention
In order to solve the problems, the invention provides a method for recycling a supported hydrogenation catalyst. The deactivated hydrogenation catalyst is regenerated and sieved, the sieved fine particles are crushed into particles with the particle size of less than 50 microns, then the particles are added into a kneading process for preparing the carrier according to a certain proportion, the particles are extruded, formed and dried, and the particles are roasted in an inert gas atmosphere to prepare a mixed carrier, the interaction between metal and the carrier is weakened by carbon in the particles, and the prepared catalyst has high hydrodesulfurization activity. The method can completely recycle the screened waste catalyst, and solves the problem of waste of the conventional screened waste catalyst as solid waste. Meanwhile, the addition amount of the organic additive is reduced, the viscosity of the impregnation liquid is reduced, the impregnation time is shortened, and the method has important industrial application value.
In order to achieve the purpose, the technical scheme of the invention is as follows:
a method for recycling a supported hydrogenation catalyst comprises the following steps:
(1) crushing the screened waste catalyst: sieving the waste hydrogenation catalyst, and then crushing the sieved fine particles into particles below 50 microns; preferably to less than 10 microns.
(2) Kneading and molding: adding the screened waste catalyst particles into the primary carrier in the kneading process, uniformly mixing, adding an acid solution for peptization, extruding into strips for forming, drying, shaping and screening, and roasting in an inert gas atmosphere to prepare a blended carrier;
(3) and (3) preparing a solution from a VIB group element-containing compound, a VIII group element-containing compound and a solvent, impregnating the mixed carrier obtained in the step (2), and drying or roasting in an inert atmosphere to obtain the hydrogenation catalyst.
Furthermore, the waste catalyst used in the step (1) is a supported catalyst which takes VIB group metal or VIB and VIIIB group binary or ternary metal as an active center, and takes composite oxide obtained by doping alumina or alumina and one or more of titanium oxide, zirconium oxide, silicon oxide, amorphous silicon aluminum, molecular sieve and zeolite as a carrier.
Further, the waste catalyst used in the step (1) has a sulfur content of not more than 1.0% and a carbon content of not more than 4.0%.
Further, the adding amount of the waste catalyst particles in the step (2) is 10-50% of the mass of the primary carrier.
Further, the preliminary carrier in the step (2) comprises pseudo-boehmite, or pseudo-boehmite mixed with one or more components of titanium oxide, zirconium oxide, silicon oxide, amorphous silicon aluminum, molecular sieve, zeolite and the like.
Further, the adding amount of the acid solution in the step (2) is 1-10% of the total mass of the carrier; the acid solution is an inorganic acid or an organic acid, wherein the inorganic acid comprises any one of sulfuric acid, phosphoric acid, hydrochloric acid and nitric acid, the organic acid comprises any one of acetic acid, oxalic acid and citric acid, the concentration of the acid solution is preferably 3-5 wt%, and the acid solution is preferably a nitric acid solution.
Further, the drying process in the step (2) is as follows: drying for 2-4 h at room temperature, and then drying for 2-4 h in an oven at 120 ℃.
Further, the roasting conditions in the inert gas atmosphere in the step (2) are specifically as follows: the inert gas is one or more of nitrogen, argon and helium, the roasting is carried out by heating from room temperature to 400-1000 ℃ at a heating rate of 10-50 ℃/min for 4 hours, preferably, the heating rate is 10 ℃/min, and the roasting temperature is 900 ℃.
Further, the compound of the group VIB element in step (3) is preferably a nickel salt, the nickel salt includes but is not limited to one or more of nickel nitrate, nickel acetate and basic nickel carbonate, and the compound of the group VIB element is preferably a molybdenum salt, and includes but is not limited to molybdate, molybdenum trioxide and the like; preferably, the nickel salt is basic nickel carbonate and the molybdenum salt is molybdenum trioxide.
Further, the solvent in the step (3) is phosphoric acid solution or phosphoric acid solution added with organic additives, and the organic additives are one or more of ethylene glycol, diethylene glycol, glycerol and citric acid.
Has the advantages that: the invention realizes the recycling of the waste catalyst by one step, and the recycling method is simple; the method overcomes the defect that the waste catalyst is used as industrial solid waste for landfill treatment, reduces the use amount of organic additives due to residual carbon on the waste catalyst, and reduces the preparation cost of the catalyst.
Detailed Description
The preparation and use of the present invention are further described with reference to the following specific examples, but the specific embodiments described herein are only for illustrating and explaining the present invention and are not intended to limit the present invention.
Example 1
Weighing 204.0g of macroporous pseudo-boehmite, uniformly mixing with 15 g of sieved waste catalyst powder, slowly adding 5wt% of nitric acid solution in the kneading process, continuously kneading for 10 min for peptizing, extruding and molding to prepare clover strips with the diameter phi of 1.45, standing for 2 h at room temperature, drying for 2 h in a 120 ℃ oven, cooling to room temperature, shaping to obtain clover strips with the length of 3-5mm, sieving by using a 20-mesh standard sieve, placing in a muffle furnace, heating from room temperature to 900 ℃ at the speed of 10 ℃/min, roasting for 4h under the nitrogen atmosphere, and naturally cooling to room temperature to obtain the blended carrier S1.
Weighing 18 g of concentrated phosphoric acid (85 wt%), dissolving in 50 g of deionized water, mixing with 34 g of molybdenum oxide and 12 g of basic nickel carbonate, and stirring and refluxing at 90 ℃ and 300r/min until the concentrated phosphoric acid is completely dissolved to prepare impregnation liquid A.
Weighing 100 g of the mixed carrier S1, soaking the soaking solution A on the carrier in an equal volume according to the water absorption of the mixed carrier S1, drying the carrier at 120 ℃ for 4 hours, and keeping the temperature at 200 ℃ for 4 hours under a nitrogen atmosphere to obtain the catalyst C1.
Example 2
Weighing 204.0g of macroporous pseudo-boehmite, uniformly mixing with 45 g of sieved waste catalyst powder, slowly adding 5wt% of nitric acid solution in the kneading process, continuously kneading for 10 min for peptizing, extruding and molding to prepare clover strips with the diameter phi of 1.45, standing for 2 h at room temperature, drying for 2 h in a 120 ℃ oven, cooling to room temperature, shaping to obtain clover strips with the length of 3-5mm, sieving by using a 20-mesh standard sieve, placing in a muffle furnace, heating from room temperature to 900 ℃ at the speed of 10 ℃/min, roasting for 4h under the nitrogen atmosphere, and naturally cooling to room temperature to obtain the blended carrier S2.
Weighing 100 g of the mixed carrier S2, soaking the soaking solution A on the carrier in an equal volume according to the water absorption of the mixed carrier S2, drying the carrier at 120 ℃ for 4 hours, and keeping the temperature at 200 ℃ for 4 hours under a nitrogen atmosphere to obtain the catalyst C2.
Example 3
Weighing 204.0g of macroporous pseudo-boehmite, uniformly mixing with 75 g of sieved waste catalyst powder, slowly adding 5wt% of nitric acid solution in the kneading process, continuously kneading for 10 min for peptizing, extruding and molding to prepare clover strips with the diameter phi of 1.45, standing for 2 h at room temperature, drying for 2 h in a 120 ℃ oven, cooling to room temperature, shaping to obtain clover strips with the length of 3-5mm, sieving by using a 20-mesh standard sieve, placing in a muffle furnace, heating from room temperature to 900 ℃ at the speed of 10 ℃/min, roasting for 4h under the nitrogen atmosphere, and naturally cooling to room temperature to obtain the blended carrier S3.
Weighing 100 g of the mixed carrier S3, soaking the soaking solution A on the carrier in an equal volume according to the water absorption of the mixed carrier S3, drying the carrier at 120 ℃ for 4 hours, and keeping the temperature at 200 ℃ for 4 hours under a nitrogen atmosphere to obtain the catalyst C3.
Example 4
Adding 15 g of ethylene glycol into the impregnation liquid A, continuously stirring and refluxing for 2 h at 90 ℃ and 300r/min, impregnating on 100 g of mixed carrier S3 in an equal volume, drying for 4h at 120 ℃, and keeping the temperature of 200 ℃ for 4h under a nitrogen atmosphere to obtain a catalyst C4.
Comparative example 1
Weighing 204.0g of macroporous pseudo-boehmite, slowly adding 5wt% of nitric acid solution in the process of kneading, continuously kneading for 10 minutes for peptizing, extruding and forming to obtain clover strips with the diameter phi of 1.45, drying for 2 hours at room temperature, drying for 2 hours in an oven at 120 ℃, cooling to room temperature, shaping to obtain clover strips with the length of 3-5mm, sieving by using a 20-mesh standard sieve, placing in a muffle furnace, raising the temperature from room temperature to 900 ℃ at the speed of 10 ℃/minute in the nitrogen atmosphere, keeping the temperature for 4 hours, and naturally cooling to room temperature to obtain the alumina carrier S4.
Soaking the soaking solution A on 100 g of alumina carrier S4 in the same volume, drying at 120 ℃ for 4h, and keeping the temperature at 200 ℃ for 4h under a nitrogen atmosphere to obtain the catalyst C5.
Comparative example 2
Adding 30 g of ethylene glycol into the impregnation liquid A, continuously stirring and refluxing for 2 h at 90 ℃ and 300r/min, impregnating on 100 g of alumina carrier S4 in an equal volume, drying for 4h at 120 ℃, and keeping the temperature constant at 200 ℃ for 4h under a nitrogen atmosphere to obtain a catalyst C6.
The carriers are respectively subjected to physicochemical property tests, and the results are shown in table 1:
TABLE 1 Carrier Properties
Figure 442578DEST_PATH_IMAGE002
From examples 1 to 3, it can be seen that the specific surface area of the blending carriers S1 to S3 was from 129 m with the increase in the amount of the waste catalyst incorporated2The/g is reduced to 98 m2(ii)/g; the pore volume is in a descending trend; the average pore diameter is not obviously changed along with the increase of the doping amount and is kept at about 16 nm; the lateral pressure strength is reduced quickly to 118N/cm at higher doping amount, but meets the requirement of industrial application. The comparative example 1 is an alumina carrier without doping a waste catalyst, compared with a doped carrier, the doping of a proper amount of the waste catalyst has little influence on the specific surface area, the pore volume, the average pore diameter and the lateral pressure strength of the carrier, and shows that the doped carrier has excellent physical and chemical properties, is suitable for serving as a catalyst carrier and simultaneously solves the problem of recycling the waste catalyst.
Application example 1: diesel oil hydrorefining reaction
The hydrofining activity evaluation of C1-C6 was carried out on a fixed bed pilot plant, the loading of the catalyst was 20 mL, and the reaction conditions were: the reaction temperature is 340 ℃, the hydrogen pressure is 9 MPa, the hydrogen-oil volume ratio is 300:1, and the space velocity is 1.5 h-1. The mixed diesel oil is used as a reaction raw material, and the properties of the mixed diesel oil are shown in the following table 2.
TABLE 2 Mixed Diesel feedstock Properties
Figure 31822DEST_PATH_IMAGE004
The catalyst test results are shown in table 3 below.
TABLE 3 catalyst test results
Figure 732930DEST_PATH_IMAGE006
The catalyst test results show that compared with the C5 without the waste catalyst, the hydrodesulfurization activity of the catalysts C1-C3 prepared by adding different amounts of waste catalysts is improved, the sulfur content of refined diesel oil is less than 10 ppm, the polycyclic aromatic hydrocarbon content is obviously reduced, and the hydrogenation performance of the catalyst is excellent. Compared with the catalyst C3, the catalyst C4 is supplemented with organic additive ethylene glycol, and the hydrogenation and desulfurization performance reaches the level of the fresh catalyst C6. In the waste catalyst mixed with the carrier, the recycling problem of the waste catalyst is solved, the addition amount of organic additives in the impregnation is reduced, the viscosity of the impregnation liquid is reduced, the uniform impregnation is facilitated, the production efficiency of the catalyst is improved, and the method has great industrial application value.
The above description is only a preferred embodiment of the present invention, and all equivalent changes and modifications made in accordance with the claims of the present invention should be covered by the present invention.

Claims (10)

1. A method for recycling a supported hydrogenation catalyst is characterized by comprising the following steps: the method comprises the following steps:
(1) crushing the screened waste catalyst: sieving the waste hydrogenation catalyst, and then crushing the sieved fine particles into particles below 50 microns;
(2) kneading and molding: adding the screened waste catalyst particles into the primary carrier in the kneading process, uniformly mixing, adding an acid solution for peptization, extruding into strips for forming, drying, shaping and screening, and roasting in an inert gas atmosphere to prepare a blended carrier;
(3) and (3) preparing a solution from a VIB group element-containing compound, a VIII group element-containing compound and a solvent, impregnating the mixed carrier obtained in the step (2), and drying or roasting in an inert atmosphere to obtain the hydrogenation catalyst.
2. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the waste catalyst used in the step (1) is a supported catalyst which takes VIB group metal or VIB and VIIIB group binary or ternary metal as an active center, and takes composite oxide obtained by doping alumina or alumina and one or more of titanium oxide, zirconium oxide, silicon oxide, amorphous silicon-aluminum, molecular sieve and zeolite as a carrier.
3. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the waste catalyst used in the step (1) has a sulfur content of not more than 1.0% and a carbon content of not more than 4.0%.
4. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: and (3) adding the waste catalyst particles in the step (2) in an amount of 10-50% of the mass of the primary carrier.
5. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the primary carrier in the step (2) comprises pseudo-boehmite, or the pseudo-boehmite is mixed with one or more components of titanium oxide, zirconium oxide, silicon oxide, amorphous silicon-aluminum, molecular sieve, zeolite and the like.
6. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the adding amount of the acid solution in the step (2) is 1-10% of the total mass of the carrier; the acid solution is inorganic acid or organic acid, wherein the inorganic acid comprises any one of sulfuric acid, phosphoric acid, hydrochloric acid and nitric acid, and the organic acid comprises any one of acetic acid, oxalic acid and citric acid.
7. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the drying process in the step (2) is as follows: drying for 2-4 h at room temperature, and then drying for 2-4 h in an oven at 120 ℃.
8. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: the roasting condition in the inert gas atmosphere in the step (2) is specifically as follows: the inert gas is one or more of nitrogen, argon and helium, and the roasting is carried out by raising the temperature from room temperature to 400-1000 ℃ at a temperature raising rate of 10-50 ℃/min and maintaining for 4 hours.
9. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: and (3) the VIB group element compound is nickel salt, and the VIB group element compound is molybdenum salt.
10. The method for recycling the supported hydrogenation catalyst according to claim 1, wherein the method comprises the following steps: and (3) the solvent is phosphoric acid solution or phosphoric acid solution added with organic additives, and the organic additives are one or a mixture of more of ethylene glycol, diethylene glycol, glycerol and citric acid.
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