CN114921261A - Method for preparing cycloparaffin aviation fuel by hydrodeoxygenation of aromatic oxygen-containing waste plastics - Google Patents

Method for preparing cycloparaffin aviation fuel by hydrodeoxygenation of aromatic oxygen-containing waste plastics Download PDF

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CN114921261A
CN114921261A CN202210444102.7A CN202210444102A CN114921261A CN 114921261 A CN114921261 A CN 114921261A CN 202210444102 A CN202210444102 A CN 202210444102A CN 114921261 A CN114921261 A CN 114921261A
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catalyst
hydrodeoxygenation
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aromatic oxygen
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刘斯宝
魏俊德
刘国柱
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Tianjin University
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    • 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
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/08Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal with moving catalysts
    • C10G1/086Characterised by the catalyst used
    • 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
    • B01J23/38Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
    • B01J23/54Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/56Platinum group metals
    • B01J23/64Platinum group metals with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/656Manganese, technetium or rhenium
    • B01J23/6567Rhenium
    • 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
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/10Feedstock materials
    • C10G2300/1003Waste materials
    • 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
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/20Characteristics of the feedstock or the products
    • C10G2300/201Impurities
    • C10G2300/202Heteroatoms content, i.e. S, N, O, P
    • 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
    • C10G2400/00Products obtained by processes covered by groups C10G9/00 - C10G69/14
    • C10G2400/08Jet fuel
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Chemical Kinetics & Catalysis (AREA)
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  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Wood Science & Technology (AREA)
  • General Chemical & Material Sciences (AREA)
  • Materials Engineering (AREA)
  • Catalysts (AREA)

Abstract

The invention relates to a method for preparing cycloparaffin aviation fuel by aromatic oxygen-containing waste plastic hydrodeoxygenation, which adopts a load-type metal-metal oxide catalyst to catalyze the aromatic oxygen-containing waste plastic hydrodeoxygenation to directly prepare the cycloparaffin aviation fuel in the presence of a solvent. The invention realizes the high-yield hydrodeoxygenation of aromatic oxygen-containing waste plastics at low temperature to prepare the naphthenic aviation fuel for the first time by the supported metal-metal oxide catalyst. The solid acid is used as a cocatalyst, so that the activity of the supported metal-metal oxide catalyst is obviously improved, and the efficiency is improved.

Description

Method for preparing cycloparaffin aviation fuel by hydrodeoxygenation of aromatic oxygen-containing waste plastics
Technical Field
The invention relates to a novel method for directly preparing naphthenic aviation fuel by taking aromatic oxygen-containing waste plastics as raw materials through hydrodeoxygenation. The supported metal-metal oxide catalyst is adopted to realize the direct hydrodeoxygenation of the aromatic oxygen-containing waste plastics under mild conditions, and a series of naphthenic aviation fuels are obtained with high yield. Compared with the prior hydrodeoxygenation method for aromatic oxygen-containing waste plastics, the method has the advantages of simple operation process, low energy consumption, low cost and the like.
Background
With the increasing use of plastic articles by humans, waste plastic has become a global problem. Polycarbonate (PC), polyethylene terephthalate (PET), polybutylene terephthalate (PBT), polyphenylene oxide (PPO), and the like, which are aromatic oxygen-containing plastic products widely used today, are mainly formed by polymerizing monomer molecules through ester group or ether bond linkage. Currently, the main method for disposing of these waste plastic products is to recycle them mechanically, but this method's deterioration of the plastic quality limits the wide application of the method, for example, only 7% of PET is recycled. Therefore, the method has positive significance for the development of environmental protection and recycling economy in order to reduce the discharge of plastics into the environment as much as possible and simultaneously degrade and convert the waste plastics into high-value chemical products.
Aviation fuel is liquid fuel with great demand in international transportation industry, and cycloalkane is an important component of aviation fuel and has very high economic value. At present, the aviation fuel is mainly prepared by taking fossil resources (coal and petroleum) as raw materials. In recent years, with the decrease of petroleum resources and the rising of international crude oil prices, the price of aviation fuel is also gradually increased. Waste plastics are used as wastes of fossil resource using terminals, and can be used as a novel resource for synthesis and preparation of aviation fuels. The aromatic oxygen-containing waste plastics can be used for preparing high-value naphthenic aviation fuel by a hydrodeoxygenation method, and the realization of the process technology not only has important significance for upgrading utilization of the waste plastics, but also can reduce the dependence on fossil resources to a certain extent.
The study on preparation of naphthenic aviation fuel by catalyzing PET and PC by adopting a two-step method is reported in the laning topic group of the major junctional complex in 2019 [ Green chem.,2019,21, 2709-2719; green chem.,2019,21,3789-3795 ]; the path includes: alcoholysis PET or PC is methyl terephthalate or bisphenol A monomer and hydrodeoxygenation monomer is cycloparaffin fuel; wherein the hydrodeoxygenation catalyst is a mixed catalyst of Ru-Cu/SiO2 and Pt/C and H-beta, and the yield of the naphthenic hydrocarbon can reach more than 80%. In order to improve the process economy, the subject group proposes that a Raney nickel and USY zeolite mixed catalyst is used for preparing naphthenic hydrocarbon and aromatic hydrocarbon fuels (C6-C15) through alcoholysis and hydrogen transfer hydrodeoxygenation, and the yield can reach 80%; however, the yield of saturated cycloalkanes is only 30% [ Green chem.,2021,23, 912-. In order to further improve the yield of target products, the subject group realizes the preparation of the dicycloalkane fuel by using a mixed catalyst of Rh/C and USY zeolite and performing one-pot water-phase hydrodeoxygenation of PC and real PC waste plastics (DVD compact discs) under the hydrogen conditions of 200 ℃ and 3MPa, wherein the yields are respectively 94.9 percent and 86.9 percent [ Green chem. 2021,23, 3693-. However, these processes require higher reaction temperatures (200 ℃) in the hydrodeoxygenation step; the most important reason is due to the low activity of the hydrodeoxygenation catalyst. Therefore, the supported metal-metal oxide hydrodeoxygenation catalyst designed and prepared by the invention can realize complete hydrodeoxygenation of aromatic oxygen-containing waste plastics at low temperature (160-200 ℃), so that the cycloparaffin aviation fuel can be prepared at high yield. In addition, the solid acid cocatalyst is added, so that the hydrodeoxygenation activity of the supported metal-metal oxide catalyst can be remarkably improved, and the efficiency of converting the aromatic oxygen-containing waste plastic into the naphthenic aviation fuel is improved.
Disclosure of Invention
The invention relates to a method for preparing naphthenic aviation fuel by catalyzing aromatic oxygen-containing waste plastics hydrodeoxygenation by using a supported metal-metal oxide bimetallic catalyst. The catalyst can enable the hydrodeoxygenation reaction to be efficiently carried out at a lower temperature, so that the reaction energy consumption is reduced. In addition, the solid acid catalyst can be used as a cocatalyst and is introduced in a physical mixing mode, so that the hydrodeoxygenation activity of the supported metal-metal oxide bimetallic catalyst can be further improved. Class M 1 -M 2 O x Catalyst type S: active ingredient M 1 Is one or more than two of metal Ru, Ir, Pd, Pt, Rh, Ni, Fe, Co and Cu; active ingredient M 2 O x For partially reduced oxides: is ReO x ,MoO x ,WO x ,VO x ,NbO x One or more than two of the above; the carrier S comprises one or more than two of silicon dioxide, ordered mesoporous silicon dioxide, activated carbon, carbon nano tubes, ordered mesoporous carbon, carbon fibers, graphene, alumina, titanium oxide, zirconium oxide and cerium oxide. Solid acid aidThe catalyst comprises: zeolite molecular sieve or mesoporous zeolite molecular sieve such as H-ZSM-5, H-Y, H-USY, H-beta, H-MOR, H-MCM-22, H-SAPO molecular sieve, etc., silica-alumina material, heteropoly acid, zirconium phosphate, zirconium tungstate, acidic clay, niobium oxy phosphate, niobium pentoxide, or acidic cation exchange resin. The catalyst of the invention can carry out hydrodeoxygenation reaction on aromatic oxygen-containing waste plastics under mild conditions. The catalyst has the characteristics of simple preparation process, low energy consumption, low cost and the like, and provides a solution for preparing the cycloparaffin aviation fuel by hydrodeoxygenation of the aromatic oxygen-containing waste plastics.
The technical scheme of the invention is as follows:
a method for preparing cycloparaffin aviation fuel by aromatic oxygen-containing waste plastics through hydrodeoxygenation adopts a load-type metal-metal oxide catalyst to catalyze aromatic oxygen-containing waste plastics to hydrodeoxygenate and directly prepare the cycloparaffin aviation fuel in the presence of a solvent.
Preferably, the supported metal-metal oxide catalyst is M 1 -M 2 O x A catalyst of the type/S; active ingredient M 1 Is one or more of metal Ru, Ir, Pd, Pt, Rh, Ni, Fe, Co and Cu; active ingredient M 2 O x For partial reduction of oxides, M 2 O x Is ReO x ,MoO x ,WO x ,VO x ,NbO x One or more of the above; the carrier S is one or more of silicon dioxide, ordered mesoporous silicon dioxide, activated carbon, carbon nano tubes, ordered mesoporous carbon, carbon fibers, graphene, aluminum oxide, titanium oxide, zirconium oxide and cerium oxide.
Preferably, the active component M 1 And an active ingredient M 2 O x The loading amounts are 0.1-20 wt% and 0.1-20 wt%, respectively.
Preferably, the reaction also comprises a cocatalyst which is a solid acid cocatalyst and is one or more of zeolite molecular sieve, mesoporous zeolite molecular sieve, silicon-aluminum material, heteropoly acid, zirconium phosphate, zirconium tungstate, acidic clay, niobium oxide phosphate, niobium pentoxide or acidic cation exchange resin, wherein the mesoporous zeolite molecular sieve comprises H-ZSM-5, H-Y, H-USY, H-beta, H-MOR, H-MCM-22 or H-SAPO molecular sieve; the addition amount of the cocatalyst is 0-500 wt% of the catalyst.
Preferably, the solvent is one of alkane or water or a mixture thereof.
Preferably, the aromatic oxygen-containing waste plastics include polycarbonate, polyethylene terephthalate, polypropylene terephthalate, polybutylene terephthalate, polyethylene isophthalate, polyethylene naphthalate, polyether ether ketone, polyether ketone, polyether ether ketone, polyether ketone ether ketone and polyphenylene ether.
Preferably, the conditions for hydrodeoxygenation of aromatic oxygen-containing waste plastics are: the temperature is 120-300 ℃, the hydrogen pressure is 0.1-20MPa, the stirring speed is 200-2000rpm, and the reaction time is 0-24 h.
Preferably, the supported metal-metal oxide catalyst is prepared by an impregnation method; the dipping method comprises the following steps: will M 1 Adding the soluble salt solution into the carrier S for isovolumetric impregnation, then drying at 50-120 ℃, and then adding M 2 Is added to the solution of the soluble salt impregnated with M 1 The carrier is dipped in the same volume, then dried at 50-120 ℃, and then roasted at 300-700 ℃ for 1-6h, thus obtaining the catalyst.
Preferably, the supported metal-metal oxide catalyst needs to be subjected to reduction treatment before use; the reduction treatment method comprises the following steps: reducing for 0.5-6 h in an intermittent reaction kettle at the temperature of 180-300 ℃ under the hydrogen atmosphere of 0.1-20 MPa; the method needs to add solvents such as cyclohexane and the like;
or, in a tubular furnace, the hydrogen atmosphere is normal pressure, the hydrogen flow rate is 10-200 ml/min, and the reduction time is 0.5-6 h at the reduction temperature of 180-500 ℃; the method is gas phase reduction.
The invention adopts the supported metal-metal oxide catalyst to realize the low-temperature hydrodeoxygenation of the aromatic oxygen-containing waste plastics to prepare the naphthenic aviation fuel; the solid acid cocatalyst is introduced in a physical mixing mode, so that the hydrodeoxygenation activity of the supported metal-metal oxide bimetallic catalyst can be further improved.
Load type metal-goldThe metal oxide catalyst may be represented by M 1 -M 2 O x Catalyst type S: active ingredient M 1 Is one or more of metal Ru, Ir, Pd, Pt, Rh, Ni, Fe, Co and Cu; active ingredient M 2 O x Is a partially reduced oxide which is ReO x ,MoO x ,WO x ,VO x ,NbO x One or more of the above; the vector S comprises: one or more of common silicon dioxide, ordered mesoporous silicon dioxide, activated carbon, carbon nanotubes, ordered mesoporous carbon, carbon fibers, graphene, aluminum oxide, titanium oxide, zirconium oxide and cerium oxide. The solid acid cocatalyst is one or more of zeolite molecular sieve, mesoporous zeolite molecular sieve such as H-ZSM-5, H-Y, H-USY, H-beta, H-MOR, H-MCM-22, H-SAPO molecular sieve, silica-alumina material, heteropoly acid, zirconium phosphate, zirconium tungstate, acidic clay, niobium phosphate, niobium pentoxide and cation exchange resin. Active ingredient M 1 0.1 to 20 wt%, preferably 1 to 5 wt%; active ingredient M 2 O x The loading amounts are respectively 0.1-20 wt%; preferably 0.2 to 5 wt%; the addition amount of the cocatalyst is 0-500 wt% of the catalyst, preferably 0-100 wt%.
The preparation of the supported metal-metal oxide catalyst adopts an impregnation method; the solid acid promoter is added by physical mixing. The impregnation method comprises the following steps: firstly, M is 1 Adding the soluble salt solution into a carrier S, soaking in a medium volume, and drying at 50-120 ℃; then M is added 2 Is added to the solution impregnated with M 1 The carrier is soaked in the same volume, then dried at 50-120 ℃, and then calcined at 300-700 ℃ for 1-6h to prepare the calcined catalyst. Wherein the preferable range of the drying temperature is 70-120 ℃, the preferable range of the roasting temperature is 350-600 ℃, and the preferable range of the roasting time is 1-4 h.
The roasted supported metal-metal oxide catalyst needs to be subjected to reduction treatment before use, and the method comprises the following steps: reducing the mixture in an intermittent reaction kettle for 0.5 to 6 hours at 180 to 300 ℃ under the hydrogen atmosphere of 0.1 to 20 MPa. Wherein the preferable range of the hydrogen pressure is 1-8 MPa, the preferable range of the reduction temperature is 180-220 ℃, and the preferable range of the reduction time is 0.5-3 h; or in a tube furnace: the hydrogen atmosphere is normal pressure, the hydrogen flow rate is 10-200 ml/min, and the reduction time is 0.5-6 h at the reduction temperature of 180-500 ℃; wherein the preferable range of the reduction temperature is 180-300 ℃, and the preferable range of the reduction time is 0.5-4 h.
The hydrodeoxygenation reaction of the aromatic oxygen-containing waste plastics is carried out in an intermittent reaction kettle, the reaction temperature is 120-300 ℃, the preferable reaction temperature is 160-200 ℃, the hydrogen pressure is 0.1-20MPa, the stirring speed is 200-2000rpm, and the reaction time is 0-24 h.
The aromatic oxygen-containing waste plastics include:
the amount of polycarbonate (PC,
Figure BDA0003615823360000051
),
polyethylene terephthalate (PET,
Figure BDA0003615823360000052
),
poly (trimethylene terephthalate) (PPT,
Figure BDA0003615823360000053
),
polybutylene terephthalate (PBT,
Figure BDA0003615823360000054
),
polyethylene naphthalate (PEN,
Figure BDA0003615823360000055
),
the polyether ether ketone (PEEK,
Figure BDA0003615823360000056
),
the polyether ketone (PEK) is a polyether ketone,
Figure BDA0003615823360000057
),
polyether ketone (PEKK,
Figure BDA0003615823360000058
),
polyetheretherketon (PEEKK,
Figure BDA0003615823360000059
),
polyetherketoneetherketoneketone (PEKEKK,
Figure BDA00036158233600000510
) And a polyphenylene oxide (PPO,
Figure BDA00036158233600000511
) Etc., or mixtures thereof.
The reaction solvent is one of alkane, water and other solvents or a mixture of water and alkane.
The invention has the beneficial effects that:
the invention realizes the high-yield hydrodeoxygenation of aromatic oxygen-containing waste plastics at low temperature to prepare the naphthenic aviation fuel for the first time by the supported metal-metal oxide catalyst. The solid acid as the promoter can be added by a physical method, so that the activity of the supported metal-metal oxide catalyst is obviously improved, the hydrodeoxygenation efficiency is improved, and the time is shortened.
Drawings
Fig. 1 and 2 are TEM images of the catalyst prepared in example 1.
FIG. 3 is a graph showing the results of the yields of catalytic degradation of waste plastics in examples 1, 5 and 6.
FIG. 4 is a GC chart of the reaction products of example 2.
FIG. 5 is a GC-MS graph of the bicycloalkane, the main product of example 2.
Detailed Description
The present invention will be further described with reference to the following examples. The following examples are only for illustrating the technical solutions of the present invention more clearly, and the protection scope of the present invention is not limited thereby.
Example 1
(1)Ru-ReO x /SiO 2 Preparation of the catalyst
Configured to take RuCl 3 The aqueous solution is added dropwise to the SiO carrier 2 Drying for 12h at a certain temperature to obtain Ru/SiO 2 And (5) producing the product. Preparing ammonium perrhenate aqueous solution, and dropwise adding Ru/SiO 2 Drying the product for 12h at a certain temperature. And transferring the obtained product to a porcelain ark, roasting the product for 3 hours at a high temperature of 500 ℃ in a muffle furnace, and naturally cooling the product to room temperature to obtain the roasted catalyst, wherein the load of Ru is 4 wt%, and the load of Re is 3.6 wt%. (15ml) is put into a high-temperature high-pressure reaction kettle and is filled with H 2 Reducing at 200 ℃ for 2h, and cooling to room temperature to obtain the metal-metal oxide Ru-ReO x /SiO 2 A catalyst. The TEM images of the prepared catalyst are shown in FIGS. 1 and 2, and it can be seen from FIGS. 1 and 2 that the Ru and Re metal particles are well dispersed in SiO 2 A surface.
(2) Waste plastic hydrodeoxygenation reaction
0.5g of PC waste plastic was charged into the cooled reaction vessel, and then the reaction vessel was sealed. At 180 ℃ H 2 The reaction was carried out at 500rpm for 20 hours. After cooling, the PC waste plastic is totally converted into C15 double alkane product
Figure BDA0003615823360000061
The yield thereof was 90% and the yield thereof was 6.5%.
Example 2
(1)Ru-ReO x /SiO 2 Preparation of the catalyst
In the same manner as in example 1, the loading of Ru was 4 wt% and the loading of Re was adjusted to 1.8 wt%. Pre-reducing catalyst, putting the roasted catalyst and cyclohexane into a high-temperature high-pressure reaction kettle, and filling H 2 Reducing at 200 deg.C for 2h, cooling to room temperature to obtain metal-metal oxide Ru-ReO x /SiO 2 A catalyst. The catalyst pre-reduction was the same as in example 1.
(2) Waste plastic hydrodeoxygenation reaction
0.5g of PC waste plastic was charged into the cooled reaction vessel, and then the reaction vessel was sealed. At 180 ℃ H 2 The reaction is carried out for 20h at a speed of 500rpm and at a pressure of 3 MPa. After cooling, the PC waste plastics are completely converted to produce C15 bicycloalkaneArticle (A)
Figure BDA0003615823360000071
The yield thereof was found to be 89% and the yield thereof was found to be 5%.
FIG. 4 is a GC graph of the reaction product of this example; as can be seen from FIG. 4, the degradation of PC is complete, and C15 bicycloalkane is the main product after the reaction, and has higher selectivity. FIG. 5 is a GC-MS diagram of the bicycloalkane as the main product of this example, which is further confirmed from the figure that the main product in FIG. 4 is C15 bicycloalkane product of the formula
Figure BDA0003615823360000072
Example 3
(1)Rh-ReO x /SiO 2 Preparation of the catalyst
Preparing rhodium nitrate aqueous solution, and dripping the rhodium nitrate aqueous solution on a carrier SiO 2 Drying for 12h at a certain temperature to obtain Rh/SiO 2 And (5) producing the product. Preparing ammonium perrhenate aqueous solution, and dropwise adding Rh/SiO 2 Drying the product for 12h at a certain temperature. And transferring the obtained product to a porcelain ark, roasting the porcelain ark for 3 hours at a high temperature of 500 ℃ in a muffle furnace, and naturally cooling the porcelain ark to room temperature to obtain the roasted catalyst, wherein the load of Rh is 4 wt%, and the load of Re is 3.6 wt%. Pre-reducing catalyst, placing calcined catalyst (0.05g) and cyclohexane (15ml) into a high-temperature high-pressure reaction kettle, and filling H 2 Reducing for 2h at 200 ℃, cooling to room temperature to obtain metal-metal oxide Rh-ReO x /SiO 2 A catalyst.
(2) Waste plastic hydrodeoxygenation reaction
The PC waste plastics are put into a cooled reaction kettle, and then the reaction kettle is sealed. At 180 ℃ and 3MPa H 2 The reaction is carried out for 16 h. After cooling, the C15 bicycloalkane product
Figure BDA0003615823360000073
The yield was 31.6% and the yield of monocycloparaffins was 1.9%.
Example 4
Hydrodeoxygenation of waste plasticsIn example 1, PC waste plastic was charged into a cooled reaction vessel, and 0.05g of HZSM-5 co-catalyst was added thereto, followed by sealing the reaction vessel. At 180 ℃ H 2 The reaction is carried out for 4 hours. After cooling, the PC waste plastic is almost completely converted to a C15 bicycloalkane product
Figure BDA0003615823360000081
The yield was 90.6% and the yield of monocycloparaffins was 6%.
Complete conversion of PC to alkane was only achieved after 20h of reaction compared to example 1; the addition of HZSM-5 co-catalyst in this example increased the reaction rate by a factor of 5, with only 4h to completely convert PC to alkane, and still maintain excellent selectivity.
Example 5
(1) Treatment of waste plastic of DVD disc
Firstly, grinding an organic layer and a metal layer of the DVD disc, then cutting the DVD disc into fragments with the size of 2 x 2mm, then placing the fragments into a beaker, respectively carrying out ultrasonic cleaning on the fragments for 30min by using deionized water and absolute ethyl alcohol, and then placing the beaker into a constant-temperature drying oven at 80 ℃ for drying.
(2) PC waste plastic hydrodeoxygenation reaction
Using the catalyst (0.05g) of example 1, the above-mentioned 0.5g of DVD disk waste plastics was charged into a cooled reaction vessel, and the reaction vessel was then sealed. At 180 ℃ H 2 And reacting for 20 hours. After cooling, the plastics are almost completely converted, C15 bicycloalkane product
Figure BDA0003615823360000082
The yield is 82 percent, and the yield of the low-carbon alkane is 6.4 percent.
Example 6
(1) Treatment of PC waste plastic plates: cutting the PC waste plastic plate into pieces with the size of 2 x 2mm, then putting the pieces into a beaker, respectively ultrasonically cleaning the pieces for 30min by using deionized water and absolute ethyl alcohol, and then putting the pieces into a constant-temperature drying oven at 80 ℃ for drying.
(2) PC waste plastic hydrodeoxygenation reaction
Using the catalyst of example 1 (0.05g), the above PC waste plastic sheet (0.5g) was charged into a cooled reaction vessel and then the reaction vessel was sealed. At 180 ℃ and 3MPa H 2 And reacting for 20 hours. After cooling, the plastics are almost completely converted, C15 bicycloalkane product
Figure BDA0003615823360000083
The yield is 92 percent, and the yield of the low-carbon alkane is 4.0 percent.
FIG. 3 is a graph showing the results of the yields of catalytic degradation of waste plastics in examples 1, 5 and 6; as can be seen from fig. 3, the catalyst prepared in example 1 can convert commercially available high purity PC chemicals or PC waste plastics, which are commonly used in life, into alkanes with high efficiency, and has excellent selectivity to bicycloalkane.
Example 7
(1) Treatment of PET waste plastic bottles: cutting the PET waste plastic bottles into pieces with the size of 2 x 2mm, then placing the PET waste plastic bottles into a beaker, respectively ultrasonically cleaning the PET waste plastic bottles for 30min by using deionized water and absolute ethyl alcohol, and then placing the cleaned PET waste plastic bottles into a constant-temperature drying box at 80 ℃ for drying.
(2) PET waste plastic hydrodeoxygenation reaction
Using the catalyst of example 1 (0.05g), 10ml of cyclohexane and 5ml of water as solvents, the above PET (0.3g) waste plastic sheet was charged into a reaction vessel and the reaction vessel was then sealed. At 200 ℃,3MPa H 2 And reacting for 20 hours. After cooling, the plastics are almost completely converted, and the yield of naphthenes is equivalent to that of the naphthenes obtained after hydrodeoxygenation of PC plastics.
The above description is only a preferred embodiment of the present invention, and it should be noted that, for those skilled in the art, several modifications and variations can be made without departing from the technical principle of the present invention, and these modifications and variations should also be regarded as the protection scope of the present invention.

Claims (9)

1. A method for preparing cycloparaffin aviation fuel by aromatic oxygen-containing waste plastic hydrodeoxygenation is characterized in that the cycloparaffin aviation fuel is directly prepared by catalyzing aromatic oxygen-containing waste plastic hydrodeoxygenation by adopting a supported metal-metal oxide catalyst in the presence of a solvent.
2. The method of claim 1, wherein the negative polarityThe supported metal-metal oxide catalyst is M 1 -M 2 O x A catalyst of the type/S; active ingredient M 1 Is one or more of metal Ru, Ir, Pd, Pt, Rh, Ni, Fe, Co and Cu; active ingredient M 2 O x For partial reduction of oxides, M 2 O x Is ReO x ,MoO x ,WO x ,VO x ,NbO x One or more of the above; the carrier S is one or more of silicon dioxide, ordered mesoporous silicon dioxide, activated carbon, carbon nanotubes, ordered mesoporous carbon, carbon fibers, graphene, aluminum oxide, titanium oxide, zirconium oxide and cerium oxide.
3. The process as claimed in claim 2, characterized in that the active component M 1 And an active ingredient M 2 O x The loading amounts are 0.1-20 wt% and 0.1-20 wt%, respectively.
4. The method of claim 1, wherein the reaction further comprises a promoter which is a solid acid promoter which is one or more of a zeolitic molecular sieve, a mesoporous zeolitic molecular sieve, a silicoaluminate, a heteropolyacid, a zirconium phosphate, a zirconium tungstate, an acidic clay, a niobium oxyphosphate, a niobium pentoxide, or an acidic cation exchange resin, the zeolitic molecular sieve or the mesoporous zeolitic molecular sieve comprising a H-ZSM-5, H-Y, H-USY, H- β, H-MOR, H-MCM-22, or H-SAPO molecular sieve; the addition amount of the cocatalyst is 0-500 wt% of the catalyst.
5. The method of claim 1, wherein the solvent is one of an alkane or water, or a mixture thereof.
6. The method according to claim 1, wherein the aromatic oxygen-containing waste plastic comprises polycarbonate, polyethylene terephthalate, polypropylene terephthalate, polybutylene terephthalate, polyethylene isophthalate, polyethylene naphthalate, polyetheretherketone, polyetherketone, polyetherketoneketone, polyetheretherketoneketone, polyetherketoneetherketoneketone, and polyphenylene ether.
7. Process according to claim 1, characterized in that the conditions for hydrodeoxygenation of aromatic oxygen-containing waste plastics are: the temperature is 120-300 ℃, the hydrogen pressure is 0.1-20MPa, the stirring speed is 200-2000rpm, and the reaction time is 0-24 h.
8. The method of claim 2, wherein the supported metal-metal oxide catalyst is prepared by an impregnation method; the impregnation method comprises the following steps: will M 1 Adding the soluble salt solution into a carrier S for isovolumetric impregnation, and then drying at 50-120 ℃; then M is added 2 Is added to the solution impregnated with M 1 The carrier is dipped in the same volume, then dried at 50-120 ℃, and then roasted at 300-700 ℃ for 1-6h, thus obtaining the catalyst.
9. The method of claim 8, wherein the supported metal-metal oxide catalyst is subjected to a reduction treatment prior to use; the reduction treatment method comprises the following steps: reducing for 0.5-6 h in a batch type reaction kettle at the temperature of 180-300 ℃ in a hydrogen atmosphere of 0.1-20 MPa; or in a tubular furnace, the hydrogen atmosphere is normal pressure, the hydrogen flow rate is 5-200 ml/min, and the reduction time is 0.5-6 h at the reduction temperature of 180-500 ℃.
CN202210444102.7A 2022-04-26 2022-04-26 Method for preparing cycloparaffin aviation fuel by hydrodeoxygenation of aromatic oxygen-containing waste plastics Pending CN114921261A (en)

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JP2014047149A (en) * 2012-08-30 2014-03-17 Tohoku Univ Method for producing tetrahydrofuran compound, and catalyst for hydrogenation and method for producing the catalyst
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WO2016067025A1 (en) * 2014-10-29 2016-05-06 Isis Innovation Limited Hydrocarbon production process
CN113441139A (en) * 2020-03-25 2021-09-28 中国石油化工股份有限公司 Hydrodeoxygenation catalyst and preparation method and application thereof
US20210348063A1 (en) * 2020-05-06 2021-11-11 Gas Technology Institute Hydrodeoxygenation of oxygenated polymers to liquid hydrocarbons

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014047149A (en) * 2012-08-30 2014-03-17 Tohoku Univ Method for producing tetrahydrofuran compound, and catalyst for hydrogenation and method for producing the catalyst
CN104119943A (en) * 2013-04-26 2014-10-29 中国科学院大连化学物理研究所 Method for preparing aviation kerosene from furyl oxygen-containing organic compounds by hydrogenation deoxidation
WO2016067025A1 (en) * 2014-10-29 2016-05-06 Isis Innovation Limited Hydrocarbon production process
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