CN108855100B - Preparation method of multifunctional metal catalyst - Google Patents

Preparation method of multifunctional metal catalyst Download PDF

Info

Publication number
CN108855100B
CN108855100B CN201810439652.3A CN201810439652A CN108855100B CN 108855100 B CN108855100 B CN 108855100B CN 201810439652 A CN201810439652 A CN 201810439652A CN 108855100 B CN108855100 B CN 108855100B
Authority
CN
China
Prior art keywords
catalyst
metal catalyst
multifunctional metal
preparation
solution
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201810439652.3A
Other languages
Chinese (zh)
Other versions
CN108855100A (en
Inventor
杨双霞
张晓东
陈雷
孙来芝
谢新苹
司洪宇
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Linyi Ulan Straw New Energy Co ltd
Original Assignee
Energy Research Institute of Shandong Academy of Sciences
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Energy Research Institute of Shandong Academy of Sciences filed Critical Energy Research Institute of Shandong Academy of Sciences
Priority to CN201810439652.3A priority Critical patent/CN108855100B/en
Publication of CN108855100A publication Critical patent/CN108855100A/en
Application granted granted Critical
Publication of CN108855100B publication Critical patent/CN108855100B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • B01J23/007Mixed salts
    • 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
    • B01J23/78Catalysts 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 alkali- or alkaline earth metals
    • 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
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/391Physical properties of the active metal ingredient
    • B01J35/393Metal or metal oxide crystallite size
    • 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
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/396Distribution of the active metal ingredient
    • B01J35/399Distribution of the active metal ingredient homogeneously throughout the support particle
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/02Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)
  • Industrial Gases (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

The preparation method of the multifunctional metal catalyst is characterized in that the catalyst is prepared by the following steps: (a) preparation of hydrotalcite precursor to laminate containingHydrotalcite single precursor of Co, Fe, Ca and Al elements; (b) calcining and reducing: weighing a certain amount of the single hydrotalcite precursor obtained in the step (a), placing the single hydrotalcite precursor in a tubular atmosphere furnace, calcining for 2-10 h at the temperature of 600-1000 ℃ in a reducing atmosphere, and naturally cooling to room temperature to obtain the multifunctional metal catalyst. The catalyst is made of Al2O3As a carrier, CoFe alloy is used as a main catalytic conversion active component, CaO is used as CO2The absorbent and the cocatalyst comprise the following components in percentage by mass: 25 to 52 percent of CoFe, 25 to 60 percent of CaO and Al2O310 to 25 percent.

Description

Preparation method of multifunctional metal catalyst
The application is a divisional application of Chinese patent application with the application date of 2016, 7, 18 and the application number of 2016105635397, namely a multifunctional metal catalyst and a preparation and application method.
Technical Field
The invention belongs to the field of energy and chemical industry, and particularly relates to Al for biomass catalytic pyrolysis2O3As a carrier, the main active component is CoFe alloy, CaO is added as CO2An absorbent and a multifunctional metal catalyst of a cocatalyst, and a preparation and application method thereof.
Background
The biomass pyrolysis gasification technology has the advantages of high efficiency, strong raw material adaptability, simple equipment and low investment, is an important aspect of biomass energy conversion technology, and is one of effective ways for cleanly and efficiently utilizing biomass energy. In the pyrolysis process of biomass, H is mainly produced2、CO、CO2、CH4And the like, and also part of organic (tar) and inorganic impurities and particles. The existence of tar not onlyResulting in a decrease in gas production rate and thermal efficiency, and also condensed into a liquid state at low temperature, and easily combined with water and dust to clog and corrode equipment. In addition, H in the gas obtained by pyrolysis and gasification of biomass2the/CO ratio is generally lower than 1, while the liquid fuel synthesis process generally requires H2the/CO ratio reaches a hydrogen-rich level of 2-3 or higher; at the same time, in order to reduce CO in the gasification gas2The influence of the efficiency and energy consumption of the subsequent synthesis gas conversion process needs to be influenced by CO2And carrying out in-situ absorption and removal. Therefore, the thermochemical conversion process of biomass needs to simultaneously solve the deep conversion of tar macromolecules and CO2Removal of H2And CO ratio adjustment.
The biomass pyrolysis steam is subjected to on-line catalytic cracking by adopting advanced catalytic materials to crack macromolecular tars to generate short-chain intermediate products and simultaneously generate more H2、CO、CO2The method has the advantages that the gasification efficiency is improved, the on-line adjustment of the components of the synthesis gas is realized, and the method is the most effective method for improving the utilization rate of the biomass and thoroughly reducing the secondary pollution. At present, the research on the catalytic pyrolysis of biomass at home and abroad mainly focuses on the selection of catalysts, and the used catalysts mainly comprise natural ore catalysts, alkali metal catalysts and transition metal-based catalysts. However, the method simply relies on a single catalyst to catalyze and crack organic macromolecules in the biomass pyrolysis process so as to simultaneously solve tar conversion and CO2Removal of H2The adjustment of the ratio of CO to CO is not ideal, and the preparation of the multifunctional catalyst with a plurality of active components superposed is imperative.
The patent "a catalyst and production method of biomass gasification furnace" (CN1686606A) discloses a catalyst and production method of biomass gasification furnace, the catalyst is composed of attapulgite clay, high alumina bauxite, ferric oxide, magnesium oxide, calcium oxide and anthracite, and the finished product is prepared by proportioning, stirring, grinding, granulating, drying, screening, detecting and packaging, and is used for thermal cracking decoking in various biomass gasification furnaces or gas furnaces, the decoking efficiency is 75%, however, the patent does not mention that the catalyst is used for CO gasification furnace and gas furnace2Absorption of (2) and H2The adjustment of the/CO ratio.
The patent 'biomass pyrolysis gasification multifunctional iron-based catalyst and preparation method thereof' (CNIO3394356A) discloses a biomass gasification multifunctional iron-based catalyst and a preparation method thereof, wherein the catalyst is prepared by adopting an impregnation method, consists of iron oxide, calcium oxide, cerium oxide and zirconium oxide, and is prepared by adding carbon monoxide (CO) into the mixture2Absorption, H2The catalyst has certain activity in the aspects of adjusting the/CO ratio and cracking tar. The method has the defects that the loading amount of the main active component iron oxide in the catalyst is low and is up to 15%, the catalyst shows high activity at 700 ℃, but is easy to gradually deactivate in the process of repeated use at high temperature (above 800 ℃), and the main reasons are that the interaction among the components of the catalyst prepared by an impregnation method is weak, and the high-content active component can migrate and grow under the high temperature condition to cause the sintering and activity reduction of the catalyst.
In the above patents, the catalytic materials all belong to a composite of iron oxide and calcium oxide, the main active components of which are mainly concentrated in a single metal (Ni or Fe). According to the research results reported by domestic and foreign documents, in tar catalytic cracking and steam reforming, metals have higher catalytic activity than oxides thereof, and particularly, alloy materials have higher catalytic activity and product selectivity than single metal catalysts. In addition, for the catalyst used in the circulating regenerated biomass moving bed gasification furnace or the fluidized bed gasification furnace, maintaining the high temperature activity stability of the catalyst is also a problem to be solved.
Hydrotalcite, also called Layered Double Hydroxide (LDHs), is an anionic Layered material with a supramolecular structure. Based on the fact that metal elements in a main body laminate can be dispersed in an atomic level according to a certain composition and proportion, the LDHs precursor method has great advantages and potentials in the aspect of preparing multifunctional catalytic materials with adjustable chemical compositions and uniform crystalline phase structures. However, at present, the application research of catalytic materials constructed based on LDHs precursors in the field of biomass pyrolysis catalytic conversion is few at home and abroad, and mainly single transition metal (Ni, Co) is used for the adjustment of tar cracking and synthesis gas composition, and no proposal is made on CO2An effective solution to the absorption problem.
Disclosure of Invention
Aiming at the problems, the invention overcomes the defects in the prior art and provides a CoFeCaAl-LDHs precursor-based catalyst which has the functions of tar cracking, synthesis gas component adjustment and CO2Multifunctional absorbing Al for biomass catalytic pyrolysis2O3And (3) loading the CoFe/CaO multifunctional metal catalyst.
The invention also provides a preparation method and an application method of the multifunctional metal catalyst.
The technical scheme adopted by the invention for solving the technical problems is as follows: a multifunctional metal catalyst for catalytic pyrolysis of biomass is prepared from Al2O3As a carrier, CoFe alloy nano particles are used as a main catalytic conversion active component, CaO is used as CO2The absorbent and the cocatalyst comprise the following components in percentage by mass: 25 to 52 percent of CoFe, 25 to 60 percent of CaO and Al2O310 to 25 percent.
The invention is characterized in that the CoFe alloy nano particles as the main active component are highly dispersed in the carrier, and the particle size is controlled to be 10-17 nm.
The multifunctional metal catalyst is prepared by the following steps:
(a) preparation of hydrotalcite precursor: mixing Ca (NO)3)2∙6H2O、Co(NO3)2∙6H2O、Al(NO3)3∙9H2O、Fe(NO3)3∙9H2Dissolving O in deionized water to prepare a solution with a concentration of [ Co ]2+]+[Ca2+]+[Fe3+]+[Al3+]A mixed salt solution of = 1-1.6M; additionally preparing NaOH solution with the concentration of 0.5-2 mol/L as a precipitator; slowly and continuously dropwise adding the prepared mixed salt solution into an alkali solution under the condition of continuous strong stirring, controlling the pH value of the final solution to be 10-11.5, and forming a suspension after dropwise adding; crystallizing for 0.5-24 h at 60 ℃, centrifuging and washing the obtained precipitation solution until the pH of the supernatant is 7, drying for 12h at 100 ℃, and grinding to obtain the hydrotalcite single precursor with the laminate containing Co, Fe, Ca and Al elements.
(b) Calcining and reducing: weighing a certain amount of the single hydrotalcite precursor obtained in the step (a), placing the single hydrotalcite precursor in a tubular atmosphere furnace, calcining for 2-10 h at the temperature of 600-1000 ℃ in a reducing atmosphere, and naturally cooling to room temperature to obtain the multifunctional metal catalyst.
A preparation method of a multifunctional metal catalyst comprises the following steps:
(a) preparation of hydrotalcite precursor: mixing Ca (NO)3)2∙6H2O、Co(NO3)2∙6H2O、Al(NO3)3∙9H2O、Fe(NO3)3∙9H2Dissolving O in deionized water to prepare a solution with a concentration of [ Co ]2+]+[Ca2+]+[Fe3+]+[Al3+]A mixed salt solution of = 1-1.6M; additionally preparing NaOH solution with the concentration of 0.5-2 mol/L as a precipitator; slowly and continuously dropwise adding the prepared mixed salt solution into an alkali solution under the condition of continuous strong stirring, controlling the pH value of the final solution to be 10-11.5, and forming a suspension after dropwise adding; crystallizing for 0.5-24 h at 60 ℃, centrifuging and washing the obtained precipitation solution until the pH of the supernatant is 7, drying for 12h at 100 ℃, and grinding to obtain the hydrotalcite single precursor with the laminate containing Co, Fe, Ca and Al elements.
(b) Calcining and reducing: weighing a certain amount of the single hydrotalcite precursor obtained in the step (a), placing the single hydrotalcite precursor in a tubular atmosphere furnace, calcining for 2-10 h at the temperature of 600-1000 ℃ in a reducing atmosphere, and naturally cooling to room temperature to obtain the multifunctional metal catalyst.
According to a particular feature of the invention, the (Co) solution in the mixed salt solution of step (a) is2++Ca2+)/(Fe3++Al3+) The molar ratio is (1-3): 1, Co2+:Ca2+:Fe3+:Al3+The molar ratio is preferably 1: 1: 1: 1 or 1: 3: 1: 1 or 1: 5: 1: 1.
the reducing atmosphere in the step (b) is hydrogen or a mixed gas of hydrogen and nitrogen or argon, wherein H in the mixed gas2The volume percentage is preferably 10%.
An application method of the multifunctional metal catalyst in the biomass catalytic pyrolysis process comprises the following steps:
(a) tabletting, crushing and screening the prepared multifunctional metal catalyst to obtain catalyst powder with the granularity of 20-100 meshes;
(b) filling biomass material in a primary reactor of a fixed bed reaction device, filling the prepared catalyst powder with the particle size of 20-100 meshes in a secondary reactor, and introducing N2Discharging air in the reaction device, simultaneously heating the reactor to a set temperature, pyrolyzing the biomass material at the temperature of 700-2Carrying the catalyst at 600-900 ℃ for catalytic cracking on the surface of the catalyst.
The invention has the beneficial effects that:
1. the invention combines the higher catalytic activity and product selectivity of CoFe alloy material and the CO to CaO2Better absorption effect, and Al is added at the same time2O3The components realize the high dispersion of active centers so as to improve the high-temperature stability of the catalyst, and the LDHs precursor method is adopted to prepare the catalyst which has the functions of tar cracking, synthesis gas component adjustment and CO2An adsorbed multifunctional metal catalyst.
2. In the invention, the loading capacity (up to 52%) and the dispersity (the particle size is 10-17 nm) of the CoFe alloy nano particles serving as the main active component of the catalyst are obviously improved, the sintering resistance and the carbon deposition resistance of the catalyst under a high-temperature condition are improved, and the catalytic activity and the high-temperature stability of the catalyst are further improved.
3. The LDHs precursor method adopted by the invention can easily realize quantitative uniform doping and composition of the final product and regulation and control of the micro-nano structure, and the synthesis method is simple, stable in chemical property and low in price, and can be applied to industrial large-scale production.
4. The multifunctional metal catalyst prepared by the invention still maintains higher catalytic activity at the catalytic cracking temperature of 900 ℃, the tar conversion rate can reach 88.82 percent, and H2The ratio of/CO is 1.86, the activity of the catalyst is kept stable within 30h of reaction, and obvious sintering and inactivation phenomena are avoided.
Detailed Description
Example 1: a preparation method of a multifunctional metal catalyst comprises the following steps:
Figure DEST_PATH_IMAGE001
according to Co2+:Ca2+:Fe3+:Al3+44.27g of Ca (NO) were weighed out in a molar ratio of 1: 13)2∙6H2O、54.56g Co(NO3)2∙6H2O、70.33g Al(NO3)3∙9H2O and 75.50g of Fe (NO)3)3∙9H2Adding O into deionized water to prepare 500 ml mixed solution, weighing 50.99g NaNO3Deionized water was added to make 500 mL of the mixed solution, and 56g of NaOH was weighed and added to make 800mL of 2M aqueous alkali. Adding NaNO3Pouring the solution and NaOH solution into a four-neck flask, dropwise adding the mixed salt solution into the mixed alkali solution under mechanical stirring to ensure that the pH of the final solution is 10.5, crystallizing the obtained slurry at 60 ℃ for 24 hours, washing with deionized water, centrifuging to obtain supernatant liquid pH =7, drying at 100 ℃ for 12 hours, and grinding to obtain LDHs precursors.
Figure 950436DEST_PATH_IMAGE002
Weighing 10g of LDHs precursor, uniformly and flatly spreading the precursor in a magnetic boat, placing the magnetic boat in a tubular atmosphere furnace, and performing reaction in a reactor N2/H2Heating to 600 ℃ at a speed of 10 ℃/min under a reducing atmosphere of (90%/10%), preserving heat for 2 hours, and naturally cooling to room temperature to obtain the multifunctional metal catalyst.
The multifunctional metal catalyst prepared by the method comprises the following components in percentage by mass: 51.86%, CaO: 25.06% of Al2O3: 23.08%, no other impurity phases were found, with the CoFe alloy nanoparticles having an average size of 10.3 nm.
An application method of the multifunctional metal catalyst in the biomass catalytic pyrolysis process comprises the following steps:
(a) tabletting, crushing and screening the prepared multifunctional metal catalyst to obtain catalyst powder with the granularity of 20-100 meshes;
(b) filling biomass material in a primary reactor of a fixed bed reaction device, filling the prepared catalyst powder with the particle size of 20-100 meshes in a secondary reactor, and introducing N2Discharging air in the reaction device, simultaneously heating the reactor to a set temperature, pyrolyzing the biomass material at 700 ℃, and generating pyrolysis steam with N of 50mL/min2Carrying the catalyst at 600-900 ℃ for catalytic cracking on the surface of the catalyst.
The typical components of the crude fuel gas produced by biomass pyrolysis gasification are (volume percentage): h2:15.06%、CO:44.28%、CO2:23.98%、CH4: 16.68% and the difference gives a tar content of 0.4429g/1g biomass.
The crude fuel gas and tar generated by the pyrolysis and gasification of the biomass with the components are subjected to online catalytic cracking, and the catalytic reaction temperature is 600 ℃. Experimental studies found that the gas components obtained after the reaction were (volume percent): h2:61.04%、CO:23.3%、CO2:8.43%、CH4: 7.23% and a tar content of 0.0201g/1g biomass. In contrast to pure pyrolysis, H2The ratio of/CO is obviously improved from 0.34 to 2.62, and the cracking rate of tar is 95.46%. The catalytic effect is higher than the performance of the catalyst reported in the literature at present. Within 30h of the reaction, the activity of the catalyst is maintained stable, the average size of CoFe alloy nano particles in the catalyst after the reaction is slightly increased to 13.3 nm, and the catalyst shows stronger high-temperature stability and anti-sintering performance.
Example 2:
the preparation method of the catalyst in this example is the same as that in example 1 and will not be described again except that the content of the active component is different, wherein Co is2+:Ca2+:Fe3+:Al3+The molar ratio is 1: 5: 1: 1. the prepared catalyst comprises the following components in percentage by mass: 25.56%, CaO: 59.86% of Al2O3: 14.58% and no other impurity phases were found, with the CoFe alloy nanoparticles having an average size of 13.7 nm。
The catalyst evaluation was carried out under the same experimental conditions as in example 1, and it was found that the gas composition obtained after the reaction was (volume percentage): h2:59.53%、CO:26.57%、CO2:3.71%、CH4:10.18%,H2The ratio of/CO was 2.24, the tar content was 0.0357g/1g biomass, and the tar cracking rate was 91.94%. The increased CaO content significantly enhanced the CO-tolerance compared to example 12The adsorption property of (2) to make CO in the synthesis gas2The content is reduced, however, the catalytic activity is reduced due to the reduction of the content of CoFe serving as a main active component, and H is caused2the/CO ratio and the tar cracking rate were slightly lowered. The average size of CoFe alloy nano particles in the catalyst after reaction is slightly increased to 17.3 nm, and the catalyst shows stronger high-temperature stability and anti-sintering performance.
Example 3:
the preparation method of the catalyst in this example is the same as that in example 1 and will not be described again, except that the preparation conditions and steps are different
Figure 929893DEST_PATH_IMAGE001
The coprecipitation pH was 9.5. To the step of
Figure 709630DEST_PATH_IMAGE001
XRD characterization of the obtained catalyst precursor shows that the product is prepared from LDHs and CaCO3Two phases are formed. The composition and mass percentage of the catalyst prepared by the precursor are close to those of the catalyst prepared in the embodiment 1, and the catalyst is CoFe: 50.46%, CaO: 26.16% of Al2O3: 23.38%, whereas the average CoFe alloy nanoparticle size increased significantly to 20.3 nm.
The catalyst evaluation was carried out under the same experimental conditions as in example 1, and it was found that the gas composition obtained after the reaction was (volume percentage): h2:46.67%、CO:27.14%、CO2:15.26%、CH4:10.93%,H2The ratio of/CO was 1.72, the tar content was 0.0494g/1g biomass, and the tar cracking rate was 88.84%. CaO vs. CO, in comparison with example 12The absorption performance is obviously reduced, and the water gas shift reaction is further reducedPromoting effect to result in H in synthetic gas2the/CO ratio is significantly reduced. In addition, CaO has weak interaction with other components in the catalyst, so that the activity of CaO in tar cracking reaction is reduced, and the tar cracking rate is slightly reduced.
Example 4:
the composition and mass percentage of the catalyst in the embodiment are consistent with those in embodiment 1, and the catalyst is CoFe: 51.86%, CaO: 25.06% of Al2O3: 23.08 percent. The preparation method is the same as that of example 1 and is not repeated herein, except that the preparation steps
Figure 104840DEST_PATH_IMAGE002
The medium catalyst has different roasting conditions, and the roasting temperature is increased by 1000 ℃ from 600 ℃. Characterization found that the average size of the CoFe alloy nanoparticles in the prepared catalyst was 16.3 nm.
The catalyst evaluation was carried out under the same experimental conditions as in example 1, and it was found that the gas composition obtained after the reaction was (volume percentage): h2:57.48%、CO:24.87%、CO2:7.72%、CH4:9.93%,H2The ratio of/CO was 2.31, the tar content was 0.0265g/1g biomass, and the tar cracking rate was 94.01%. Compared with example 1, even when the roasting temperature is raised to 1000 ℃, the CoFe alloy particles of the main active component of the catalyst do not have sintering phenomenon and have obvious size increase, so that the high catalytic activity, H, is still maintained2the/CO ratio and the tar cracking rate were slightly lowered. After the reaction, the average size of the CoFe alloy nano particles in the catalyst is increased to 24.3 nm, and the catalyst shows stronger sintering resistance.
Example 5:
the composition and mass percentage of the catalyst in the embodiment are consistent with those in embodiment 1, and the catalyst is CoFe: 51.86%, CaO: 25.06% of Al2O3: 23.08%, no other impurity phases were found, with the CoFe alloy nanoparticles having an average size of 10.3 nm. The preparation method is the same as that of example 1, and the details are not repeated here.
The difference from the example 1 is that the pyrolysis temperature of the biomass is increased from 700 ℃ to 900 ℃, and the catalytic reaction temperature isAt 600 ℃, the gas components obtained after the reaction are found to be (volume content): h2:59.57%、CO:20.83%、CO2:7.72%、CH4:11.88%,H2The ratio of CO/tar was 2.86, the tar content was 0.0068g/1g biomass, and the tar cracking rate was 98.46%. Compared with the embodiment 1, when the pyrolysis temperature of the biomass is increased to 900 ℃, part of tar macromolecular organic compounds in the pyrolysis gas are decomposed under the high-temperature condition and are further subjected to catalytic cracking under the action of the catalyst, so that the quality of the synthesis gas and the cracking rate of the tar are further improved, however, the energy consumption of the system is increased when the pyrolysis temperature is increased, and the method is not beneficial to practical industrial application. The catalyst has no obvious change in structure after long-time reaction operation, and shows high heat stability and sintering resistance.
Example 6:
the composition and mass percentage of the catalyst in the embodiment are consistent with those in embodiment 1, and the catalyst is CoFe: 51.86%, CaO: 25.06% of Al2O3: 23.08%, no other impurity phases were found, with the CoFe alloy nanoparticles having an average size of 10.3 nm. The preparation method is the same as that of example 1, and the details are not repeated here.
The difference from example 1 is that the catalytic reaction temperature is raised from 600 ℃ to 900 ℃, and the biomass pyrolysis temperature is still 700 ℃. The gas components obtained after the reaction are found to be (volume percentage): h2:45.08%、CO:24.32%、CO2:18.72%、CH4:11.88%,H2The ratio of/CO was 1.86, the tar content was 0.0495g/1g biomass, and the tar cracking rate was 88.82%. When the catalytic temperature was increased to 900 ℃ the catalytic activity was reduced compared to example 1, whereas the resulting H2The ratio of CO to the oil and tar cracking rate is still higher than the results reported in most literatures. Within 30h of the reaction, the activity of the catalyst is maintained stable, the average size of the CoFe alloy nano particles in the catalyst after the reaction is increased to 21.8 nm, and the catalyst shows stronger sintering resistance.

Claims (5)

1. The preparation method of the multifunctional metal catalyst is characterized by comprising the following steps:
(a) preparation of hydrotalcite precursor: mixing Ca (NO)3)2∙6H2O、Co(NO3)2∙6H2O、Al(NO3)3∙9H2O、Fe(NO3)3∙9H2Dissolving O in deionized water to prepare a solution with a concentration of [ Co ]2+]+[Ca2+]+[Fe3+]+[Al3+]A mixed salt solution of = 1-1.6M; additionally preparing NaOH solution with the concentration of 0.5-2 mol/L as a precipitator; slowly and continuously dropwise adding the prepared mixed salt solution into an alkali solution under the condition of continuous strong stirring, controlling the pH value of the final solution to be 10-11.5, and forming a suspension after dropwise adding; crystallizing for 0.5-24 h at 60 ℃, centrifuging and washing the obtained precipitation solution until the pH of the supernatant is 7, drying for 12h at 100 ℃, and grinding to obtain a hydrotalcite single precursor with a laminate containing Co, Fe, Ca and Al elements;
(b) calcining and reducing: weighing a certain amount of the single hydrotalcite precursor obtained in the step (a), placing the single hydrotalcite precursor in a tubular atmosphere furnace, calcining for 2-10 h at the temperature of 600-1000 ℃ in a reducing atmosphere, and naturally cooling to room temperature to obtain a multifunctional metal catalyst;
multifunctional metal catalyst with Al2O3As a carrier, CoFe alloy nano particles are used as a main catalytic conversion active component, CaO is used as CO2The absorbent and the cocatalyst comprise the following components in percentage by mass: 25 to 52 percent of CoFe, 25 to 60 percent of CaO and Al2O310 to 25 percent.
2. The method for preparing a multifunctional metal catalyst according to claim 1, wherein the (Co) mixed salt solution in the step (a) is2++Ca2+)/(Fe3++Al3+) The molar ratio is (1-3): 1, Co2+:Ca2+:Fe3+:Al3+The molar ratio is 1: 1: 1: 1 or 1: 3: 1: 1 or 1: 5: 1: 1.
3. the method of preparing a multifunctional metal catalyst according to claim 1, wherein the reducing atmosphere in the step (b) is hydrogen, or a mixture of hydrogen and nitrogen or argon.
4. The method of claim 1, wherein the volume percentage of hydrogen in the mixed gas is 10%.
5. The method for preparing a multifunctional metal catalyst according to claim 1, wherein the CoFe alloy nanoparticles as the main active component are highly dispersed in the carrier, and the particle diameter thereof is controlled to be 10-17 nm.
CN201810439652.3A 2016-07-18 2016-07-18 Preparation method of multifunctional metal catalyst Expired - Fee Related CN108855100B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810439652.3A CN108855100B (en) 2016-07-18 2016-07-18 Preparation method of multifunctional metal catalyst

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN201610563539.7A CN106238061B (en) 2016-07-18 2016-07-18 Multi-function metal catalyst and methods for making and using same
CN201810439652.3A CN108855100B (en) 2016-07-18 2016-07-18 Preparation method of multifunctional metal catalyst

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
CN201610563539.7A Division CN106238061B (en) 2016-07-18 2016-07-18 Multi-function metal catalyst and methods for making and using same

Publications (2)

Publication Number Publication Date
CN108855100A CN108855100A (en) 2018-11-23
CN108855100B true CN108855100B (en) 2020-11-24

Family

ID=57613851

Family Applications (3)

Application Number Title Priority Date Filing Date
CN201810439652.3A Expired - Fee Related CN108855100B (en) 2016-07-18 2016-07-18 Preparation method of multifunctional metal catalyst
CN201810439092.1A Expired - Fee Related CN108686664B (en) 2016-07-18 2016-07-18 Application method of multifunctional metal catalyst in biomass catalytic pyrolysis process
CN201610563539.7A Active CN106238061B (en) 2016-07-18 2016-07-18 Multi-function metal catalyst and methods for making and using same

Family Applications After (2)

Application Number Title Priority Date Filing Date
CN201810439092.1A Expired - Fee Related CN108686664B (en) 2016-07-18 2016-07-18 Application method of multifunctional metal catalyst in biomass catalytic pyrolysis process
CN201610563539.7A Active CN106238061B (en) 2016-07-18 2016-07-18 Multi-function metal catalyst and methods for making and using same

Country Status (1)

Country Link
CN (3) CN108855100B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110227468B (en) * 2019-07-15 2022-11-15 山东省科学院能源研究所 Preparation of nickel-calcium based composite catalyst and application of nickel-calcium based composite catalyst in biomass catalytic pyrolysis process
CN112569896B (en) * 2020-12-07 2023-08-25 华东理工大学 Calcium oxide-based bimetal composite material, preparation method and application
CN114653372B (en) * 2022-03-07 2023-05-26 国网综合能源服务集团有限公司 Preparation method of high-dispersion nickel-based catalyst and application of high-temperature water gas shift reaction catalyzed by high-dispersion nickel-based catalyst
CN116251595B (en) * 2023-02-09 2024-04-26 中国石油大学(华东) Calcium aluminate-based multi-metal composite material and preparation method and application thereof
CN117431082B (en) * 2023-12-11 2024-03-08 成都万潜科延科技有限公司 Catalytic carbonization method of tar generated by biomass pyrolysis, carbon material and application

Family Cites Families (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5335790B2 (en) * 1973-12-05 1978-09-28
CN1301789C (en) * 2005-02-25 2007-02-28 许庆华 Biomass gasification catalyst and its production method
CN101143327B (en) * 2006-09-13 2010-09-29 中国科学院生态环境研究中心 Nitrogen oxide storing catalyst with waterlike talc as precursor
CN101468316A (en) * 2007-12-24 2009-07-01 湖南众薪生物能源科技有限公司 Catalyst for promoting conversion of coke tar in biomass gas and preparation method thereof
EP2105486A1 (en) * 2008-03-25 2009-09-30 KiOR Inc. Low total acid number bio-crude
CN102574114B (en) * 2009-04-22 2015-12-02 科伊奥股份有限公司 The pyrolysis catalysts of controlled activity
KR101140340B1 (en) * 2009-11-17 2012-05-03 한국에너지기술연구원 Method of hydrocarbon production from biological origins using hydrotalcites as catalysts
US8921628B2 (en) * 2011-03-10 2014-12-30 Kior, Inc. Refractory mixed-metal oxides and spinel compositions for thermo-catalytic conversion of biomass
FI125582B (en) * 2013-03-08 2015-12-15 Upm Kymmene Corp Process for converting gaseous products
CN103157469A (en) * 2013-04-11 2013-06-19 北京化工大学 Supported bimetal nanocrystal catalyst and preparation method thereof
CN104148081B (en) * 2013-08-20 2016-05-11 山东省科学院能源研究所 The multi-functional ferrum-based catalyst of biomass pyrogenation gasification

Also Published As

Publication number Publication date
CN106238061A (en) 2016-12-21
CN108855100A (en) 2018-11-23
CN108686664A (en) 2018-10-23
CN108686664B (en) 2020-10-20
CN106238061B (en) 2018-07-31

Similar Documents

Publication Publication Date Title
CN108855100B (en) Preparation method of multifunctional metal catalyst
Yu et al. Engineering an effective MnO2 catalyst from LaMnO3 for catalytic methane combustion
Chen et al. Hydrogen production from ethanol steam reforming: effect of Ce content on catalytic performance of Co/Sepiolite catalyst
Ermakova et al. Effective catalysts for direct cracking of methane to produce hydrogen and filamentous carbon: Part I. Nickel catalysts
Song et al. Effects of preparation methods of ZrO2 support on catalytic performances of Ni/ZrO2 catalysts in methane partial oxidation to syngas
Xu et al. Catalytic performances of NiO–CeO2 for the reforming of methane with CO2 and O2
Qingli et al. Ni supported on MgO modified attapulgite as catalysts for hydrogen production from glycerol steam reforming
Ai et al. Probing the promotional roles of cerium in the structure and performance of Cu/SiO 2 catalysts for ethanol production
Tan et al. Ni-Mg-Al solid basic layered double oxide catalysts prepared using surfactant-assisted coprecipitation method for CO2 reforming of CH4
CN110227468B (en) Preparation of nickel-calcium based composite catalyst and application of nickel-calcium based composite catalyst in biomass catalytic pyrolysis process
Calgaro et al. Decomposition of methane over Co3− xAlxO4 (x= 0–2) coprecipitated catalysts: The role of Co phases in the activity and stability
Awadallah et al. Effect of combining Al, Mg, Ce or La oxides to extracted rice husk nanosilica on the catalytic performance of NiO during COx-free hydrogen production via methane decomposition
Jin et al. Ni/MgOAl2O3 catalyst derived from modified [Ni, Mg, Al]-LDH with NaOH for CO2 reforming of methane
Yang et al. Effects of Cu and Fe additives on low-temperature catalytic steam reforming of toluene over Ni/AC catalysts
CN108579750B (en) Copper-doped Ni/SiO2Nano composite catalyst and preparation method thereof
Hui et al. NiO@ SiO2 core-shell catalyst for low-temperature methanation of syngas in slurry reactor
Burri et al. High surface area TiO 2–ZrO 2 prepared by caustic solution treatment, and its catalytic efficiency in the oxidehydrogenation of para-ethyltoluene by CO 2
Xie et al. The relationship between the microstructures and catalytic behaviors of iron–oxygen precursors during direct coal liquefaction
Gupta et al. Coal fly ash‐derived mesoporous SBA‐15 as support material for production of liquid hydrocarbon through Fischer–Tropsch route
Khan et al. CO2 reforming of methane over activated carbon-Ni/MgO-Al2O3 composite catalysts for syngas production
Peng et al. SnO2 nano-sheet as an efficient catalyst for CO oxidation
Habimana et al. Effect of Cu promoter on Ni-based SBA-15 catalysts for partial oxidation of methane to syngas
CN113842918B (en) High-activity anti-sintering methane steam reforming catalyst and preparation method and application thereof
Salmones et al. Pore geometry influence on the deactivation behavior of Ni-based catalysts for simultaneous production of hydrogen and nanocarbon
Bhosale et al. Solar thermochemical water-splitting for H2 generation using sol-gel derived ferrite nanomaterials

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
TR01 Transfer of patent right

Effective date of registration: 20230601

Address after: 273400 meters east of Beiwang Guantuan Village, Tanyi Town, Fei County, Linyi City, Shandong Province

Patentee after: Linyi Ulan Straw New Energy Co.,Ltd.

Address before: 250014 No. 19, ASTRI Road, Lixia District, Shandong, Ji'nan

Patentee before: ENERGY Research Institute OF SHANDONG ACADEMY OF SCIENCES

TR01 Transfer of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20201124