CN106492873A - A kind of catalyst for bio oil upgrading - Google Patents

A kind of catalyst for bio oil upgrading Download PDF

Info

Publication number
CN106492873A
CN106492873A CN201611023688.0A CN201611023688A CN106492873A CN 106492873 A CN106492873 A CN 106492873A CN 201611023688 A CN201611023688 A CN 201611023688A CN 106492873 A CN106492873 A CN 106492873A
Authority
CN
China
Prior art keywords
catalyst
upgrading
bio oil
oil
high temperature
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.)
Granted
Application number
CN201611023688.0A
Other languages
Chinese (zh)
Other versions
CN106492873B (en
Inventor
韩先福
王红军
贺伟力
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.)
Beijing Union Green Technology Group Co ltd
Original Assignee
New Austrian Ecological Environment Management Co Ltd
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 New Austrian Ecological Environment Management Co Ltd filed Critical New Austrian Ecological Environment Management Co Ltd
Priority to CN201611023688.0A priority Critical patent/CN106492873B/en
Publication of CN106492873A publication Critical patent/CN106492873A/en
Application granted granted Critical
Publication of CN106492873B publication Critical patent/CN106492873B/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
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/40Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively
    • B01J29/42Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of the pentasil type, e.g. types ZSM-5, ZSM-8 or ZSM-11, as exemplified by patent documents US3702886, GB1334243 and US3709979, respectively containing iron group metals, noble metals or copper
    • B01J29/46Iron group metals or copper
    • 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
    • C10G3/00Production of liquid hydrocarbon mixtures from oxygen-containing organic materials, e.g. fatty oils, fatty acids
    • C10G3/42Catalytic treatment
    • C10G3/44Catalytic treatment characterised by the catalyst used
    • C10G3/48Catalytic treatment characterised by the catalyst used further characterised by the catalyst support
    • C10G3/49Catalytic treatment characterised by the catalyst used further characterised by the catalyst support containing crystalline aluminosilicates, e.g. molecular sieves
    • 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
    • Y02P30/00Technologies relating to oil refining and petrochemical industry
    • Y02P30/20Technologies relating to oil refining and petrochemical industry using bio-feedstock

Abstract

The invention provides a kind of catalyst for bio oil upgrading, the catalyst is the ferrum-based catalyst of silicate load.The catalyst is particularly conducive to for the bio oil that high temperature garbage distills carbonization generation to carry out hydrogenation upgrading.Bio oil after upgrading has relatively low oxygen content and higher calorific value.

Description

A kind of catalyst for bio oil upgrading
Technical field
The invention belongs to catalyst technical field, and in particular to a kind of catalyst for bio oil upgrading.
Background technology
Bio oil crude quality is generally poor, needs to meet demanded fuel through successive modified upgrading.Bio oil is carried Matter mainly includes that hydrogenation deoxidation, catalytic cracking, catalytic reforming and catalytic esterification, catalysis upgrading can change the composition of bio oil, Fundamentally change the quality of bio oil.The key technologies such as yield and efficiency in production need to be broken through, and develop efficient catalytic Agent is the emphasis of bio oil upgrading from now on and difficult point.
At present, up to 1.8 hundred million tons of the annual production of China's domestic waste, rubbish annual production about 440 is public per capita in city Jin, and rapidly increased with the speed more than 10% every year, it is predicted that the year two thousand thirty, Municipal Solid Waste in China annual production are up to 4.09 hundred million tons.The refuse production per capita of big and medium-sized cities, especially megalopolis is of a relatively high, and it is left that its rate of rise reaches 20% Right.
If to these rubbish can not be appropriate process and disposal, (heavy metal, cause of disease are micro- for that poisonous and harmful substance therein Biology etc.) will be entered in ecosystem by certain surrounding medium such as soil, air, earth's surface or subsoil water and form dirt Dye.This not only can destroy ecological environment, cause irreversible Ecological Changes, but also animals and plants safety and the mankind can be good for Health works the mischief.
Garbage disposal at present can only reduce waste volumes by burning disposal.It is each that burning disposal method can produce two English etc. Environmentally hazardous polluter is planted, the garbage incineration equipment price height of safety, scale of investment are big, and burning disposal can only pass through Handling is used for maintaining to run, and in conventional rubbish, resin, Plastic account for 10% or so, and remaining is exactly kitchen, paper, wood chip etc..
CN102218324A discloses a kind of catalyst for bio oil catalysis upgrading and preparation method, including catalyst Active component and catalyst carrier, by mass percentage, the catalyst active component and catalyst carrier are consisted of: NiO is 10-32wt%;MoO3For 5-18wt%;CoO is 5-15wt%;Remaining it is divided into dolomite catalysts carrier.
CN104722329A discloses the catalyst that a kind of bio-oil catalytic hydrogenation prepares alkane, with content as 10%~ 50% base metal nickel slaine, molybdenum salt, cobalt slaine, tungsten slaine are used as active component, modified molecular screen/oxidation Aluminum is used as catalyst carrier;By catalyst carrier support content be 10%~50% molybdenum, nickel, cobalt, in tungsten one or two with Upper mixing, obtains bio-oil Hydrobon catalyst presoma;The presoma is activated under 300-600 DEG C of hydrogen atmosphere 2- 6h, obtains the catalyst that bio-oil catalytic hydrogenation prepares alkane.
CN105854872A discloses a kind of catalyst for biological oil hydrodeoxygenation and preparation method thereof, preparation method For:Learnt from else's experience the catalyst carrier for being impregnated with active component of roasting so as to adsorb oxygen-containing inorganic acid, and through high temperature drying at Reason, carries out vulcanizing treatment afterwards, obtains final product product;Wherein, the active component mainly by one or more in VB races metal with One or more composition in VIIB races metal.
CN105413723A discloses a kind of preparation method of the Ni-based biological oil hydrodeoxygenation catalyst of non-loading type, belongs to Catalyst synthesis technology field.First, by surfactant, carbamide and soluble nickel salt, solubility microcosmic salt or (and) solubility Tungsten salt uses water dissolution respectively, 2~16h of crystallization under the conditions of 100~300 DEG C, then by filtration after filtering residue respectively with water and nothing Water-ethanol is washed, and obtains final product non-loading type nickel-base catalyst, be finally put into non-loading type nickel-base catalyst and bio oil after drying In batch reactor, hydrogenation deoxidation is carried out under the conditions of 2~4MPa of Hydrogen Vapor Pressure, 100~250 DEG C of temperature and reacts 1~10h, obtained Arrive biological oil hydrodeoxygenation product.
CN104841466A discloses a kind of biological oil base oxygenatedchemicalss hydrogenation deoxidation catalyst, including carrier and load Catalyst component on carrier, carrier are silicon dioxide, and active component is the metal phosphide and noble metal being closely contacted with each other, Metal phosphide is nickel phosphide or phosphating sludge, and noble metal is palladium, platinum or ruthenium, and the weight/mass percentage composition of above-mentioned each component is:Metal Phosphide 5~15%, noble metal 0.1~1.0%, balance of carrier.
CN103949281A discloses the molecular sieve carried NiO catalyst systems of ultrasonic assistant pyrolysis bio-oils Modified MCM-41 Preparation Method and application belong to bio oil modification technology;Will be with analytically pure Ni (NO3)2·6H2The nitric acid that O is prepared with deionized water Nickel solution supersound process at 45 DEG C, while the MCM-41 molecular sieve solids powder for accounting for nickel nitrate solution gross weight 8% is added To in nickel nitrate solution, to add and continue supersound process 30 minutes after terminating, then stand 30 minutes, then dry at 100 ± 5 DEG C Do, crush, cross 40 mesh sieves, roasting 3 hours, obtain catalyst at 550 DEG C.
CN 104888766A disclose a kind of hydrogenation deoxidation catalyst, and the catalyst is passed through by hydrogenation active metals component Infusion process is supported on carrier and is obtained, and the carrier is ordered mesopore carbon/oxidation aluminium silicon composite material;With carbon, silicon oxide and oxygen Change aluminum mass percent sum for 100% meter, carbon 10-80%, balance of silicon oxide and aluminium oxide, wherein silica alumina ratio is 7- 300;The specific surface area of the catalyst is 200-450m2/ g, pore volume are 0.20-0.40cm3/ g, aperture are 3.0-6.0nm.
WO2012/166402A1 is disclosed for by the embodiment party of the method for biomass derived pyrolysis oil deoxidation and catalyst Case, the method comprising the steps of:Make biomass derived pyrolysis oil with the first dehydrogenation catalyst under the first predetermined hydroprocessing condition Contacted to form the derivative pyrolysis oil effluent of the first hypoxic bio matter in the presence of hydrogen gas, the first dehydrogenation catalyst includes neutrality Catalyst carrier, nickel, cobalt and molybdenum, nickel of first dehydrogenation catalyst comprising the amount for calculating 0.1-1.5 weight % as oxide.
US2009/062241A1 discloses a kind of method that solid biomass is changed into hydrocarbon, including a) being about 50 DEG C The solid biomass is made to contact with catalyst in the first riser operated to about 200 DEG C of temperature, biological so as to produce first Matter-catalyst mixture and the first hydrocarbonaceous product;B) first product is separated from first biomass-catalyst mixture Thing;C) by first biomass-catalyst mixture be added to about 200 DEG C to about 400 DEG C temperature operate the second riser In, so as to produce the second biomass-catalyst mixture and the second hydrocarbonaceous product;D) mixed from second biomass-catalyst Compound separates second product;E) by second biomass-catalyst mixture be added to greater than about 450 DEG C temperature operate In 3rd riser, so as to produce dead catalyst and hydrocarbonaceous third product;And from the dead catalyst, f) isolate the 3rd stream Go out thing.
" Fast Pyrolysis of Biomass for Producing Bio-oil ", Zhu Xifeng etc., scientific and technological Leader, 2007,25 (21):69-75, by unit Element analysis and modified oil structural analyses can hold the effect of catalytic hydrogenation on the whole, while in for research biomass crude oil There is the good theoretical direction of hydrogenation deoxidation reaction offer former so as to improve biomass under the catalytic condition of MoS2 in one-component Oily yield.
However, in above-mentioned document and other prior arts, the bio oil for using is produced usually from agricultural products, forestry Product, water plant, the bio oil that these bio oil are obtained with domestic waste distillation carbonization have in composition and in nature larger Difference, still lacking, the bio oil for distilling carbonization acquisition from domestic waste effectively can be carried out the catalysis of effective upgrading Agent.
Content of the invention
For solving the above problems, the present inventor passes through and gos deep into and systematic study, fully analyzes from domestic waste The composition of the bio oil that distillation carbonization is obtained and property, there is provided technical scheme below, effectively enter to the bio oil Hydrogenation upgrading is gone, it is achieved thereby that the recycling treatment of rubbish and utilization.
In one aspect of the invention, there is provided a kind of catalyst for bio oil upgrading, the catalyst is negative for silicate The ferrum-based catalyst of load.
Preferably, the silicate is molecular sieve.It is highly preferred that the molecular sieve is HZSM-5 molecular sieves.
In a particularly preferred embodiment of the present invention, the present inventor develops a kind of energy through numerous studies The enough catalysis for effectively carrying out hydrogenation upgrading to the bio oil in the gas stream from domestic waste high temperature distillation carbonization Agent, active component of the catalyst comprising carrier and load on the carrier, the catalyst can be the catalysis shown in following formula Agent:Ni-Cu-Pd-Co2O3-Fe2O3The mol ratio of/HZSM-5, wherein Ni, Cu, Pd, Co, Fe is (1-2):(5-10):(0.1- 0.5):(1-2):(10-20), based on overall catalyst weight gauge, Ni-Cu-Pd-Co2O3-Fe2O3The content of active component is 1- 10%, preferably 2-8%, more preferably 3-6%, further preferred 5%, HZSM-5 are carrier.
Preferably, HZSM-5 for low silica-alumina ratio HZSM-5, for example silica alumina ratio be less than 15, more preferably less than 10, this be because For finding that acid strong HZSM-5 is more beneficial for the cracking of bio oil heavy component, bio oil bottoms are minimum.
The composition of bio oil is usually relatively complex, and mainly may include acids, aldehydes, ketone, alcohols, phenols, furans, ester Class, ethers and a small amount of nitrogen-containing compound and other multi-functional compounds.As bio oil heat stability is poor, acid and corrosivity By force, water content is high, calorific value is low and is difficult the characteristic such as to dissolve each other with petroleum-based products, therefore at present bio oil can only realize primary should With for example for the heat power equipment such as Industrial Stoves and oil burning boiler, it is impossible to which petroleum replacing product directly applies to internal combustion engine or turbine The burning of machine, it is impossible to meet modern high-grade commercial Application.In order to improve bio oil application, need to be transformed into Gao Pin The liquid fuel of position, reaches the requirement of transport fuel, and so as to realize substituting or part petroleum replacing product, this just must be to biology Oil is modified upgrading so as to which chemical constituent is converted into Hydrocarbon by hydrocarbon oxygen compound.How effectively to bio oil Carry out the exploitation that one of key of upgrading is catalyst.
Research finds, in the above-mentioned catalyst of the present invention, Niδ+Than conventional Moδ+There is higher activity, Ni makes With can obtain C6-C12 hydrocarbon (preferably alkane) with high selectivity, the use of Cu can obtain C16 hydrocarbon (preferred alkane with high selectivity Hydrocarbon), use while Ni, Cu, it has surprisingly been found that it may also be ensured that obtaining a certain amount of C18 and C19 hydrocarbon, surface Ni, Cu make Effectively there are hydrogenolysis with the C-O keys in bio oil can be made.
Different from general improving quality of biomass oil, in the gas stream of the present invention, the steam containing higher proportion, therefore Very high request is proposed to the hydrothermal stability of catalyst.The conventional catalyst for improving quality of biomass oil cannot be used for this The upgrading of the gas stream of invention.Iron catalyst is a kind of common catalyst for removing oxygen in plant base material, but ferrum catalysis Agent is failed when meeting water, although and palladium catalyst when meeting water effectively, the effect of its deoxygenation be not fine, and costly, and Minimal amount of palladium is added in ferrum, can obtain good synergism.Inventor's research finds that the addition of a small amount of palladium contributes to hydrogen Be covered in the surface of ferrum in catalyst, make reaction accelerate, and prevent water blocking react, thus hydrogen consumption little, activity, stability and Far better than single iron catalyst in terms of selectivity, its catalytic life can improve more than 2 times.
Through research, the present inventor also has found that the addition of Co advantageously reduces the crystallite dimension of catalytic active component so as to energy Enough it is effectively embedding in the duct of HZSM-5 molecular sieves, this is for improving the activity of catalytic active component, selectivity and stable Property has very positive meaning.However, if Co amounts are excessive, Co can cover hydrogenation sites Ni, Cu etc., so as to reduce urging The activity of agent.
Contain more non-aromatic hydro carbons in the bio oil of gas stream, the acid centre on HZSM-5 molecular sieves can It is aromatic compound effectively by the non-aromatic hydrocarbon conversion.Acetyl of the carboxylic acid major part in bio oil from hemicellulose Base, its thermal decomposition product are mainly acetic acid, and HZSM-5 molecular sieves have preferable decarboxylation ability, and the carboxylic acid in bio oil is in molecular sieve There is decarboxylic reaction and deoxygenation under catalytic action so that carboxylic acid content is greatly decreased in the bio oil after upgrading.
Previously there is not been reported in document for above-mentioned particularly a preferred catalyst, and which is that the present invention is directed to from garbage reclamation The concrete composition feature of gas stream and bio oil is targetedly designed, and achieves good upgrading effect.
The catalyst can be prepared using the conventional dipping calcination method in this area.Specifically, weigh according to the above ratio A certain amount of precursor salt such as Ni (NO3)2、Cu(NO3)2、Pd(NO3)2、Co(NO3)2、Fe(NO3)3(or their hydrate forms) And citric acid, plus deionized water dissolving, stir, be made into the solution that concentration is 0.5-1.5mol/L, weigh a certain amount of HZSM-5 molecular sieves are put in reaction vessel, and the solution for preparing is poured in reaction vessel, are placed in the constant temperature with agitator and are added Heating in deep fat bath apparatus, at a temperature of 60-120 DEG C stirs 1h-10h, is then placed in 100 DEG C of -150 DEG C of dryings in drying baker The catalyst precursor for obtaining subsequently is placed in 500 DEG C -800 DEG C calcining 1h-6h in Muffle furnace, then in H by 12h2In the presence of in Reduction activation at 200-300 DEG C, is obtained Ni-Cu-Pd-Co2O3-Fe2O3/ HZSM-5 catalyst.
In another aspect of this invention, there is provided application of the above-mentioned catalyst in bio oil upgrading.
The bio oil is preferred from composting charing process.
In grading process, the bio oil can be carried in the form of the gaseous stream comprising bio oil and water vapour Matter.That is, the logistics comprising bio oil and vapor is directly carried out upgrading, need not isolate bio oil carries out upgrading again.
The upgrading is preferably and is hydrogenated with upgrading, more preferably hydrogenation deoxidation upgrading.
For the present invention, 3.0wt.% is preferably shorter than through the content of unsaturated phenol in the bio oil of upgrading.
Preferably, bio oil and water through upgrading will be isolated from logistics after upgrading.
It is highly preferred that the separation is carried out by distillating method.
For the present invention, the composting charing process may include following steps:(1) rubbish loading rubbish is transported Device;(2) rubbish feeding device is made to pass through high temperature distillation carbonizing apparatus;(3) gas is taken out from high temperature distillation carbonizing apparatus top Logistics, the gas stream include bio oil and vapor;(4) gas stream is made to pass through catalyst bed in a gaseous form;(5) will Condensed from the effluent of catalyst bed and separated, obtained bio oil and the water through upgrading;(6) from through high temperature distillation charcoal The rubbish feeding device that makeup is put obtains charcoal class material.
The rubbish is preferably domestic waste.
Gas stream is taken out preferably in a continuous manner from high temperature distillation carbonizing apparatus top.
High temperature distillation carbonizing apparatus is heated by high temperature anaerobic steam.
The temperature of the high temperature anaerobic steam is preferably 300-600 DEG C.The pressure of the high temperature anaerobic steam is preferably 0.1-1.0MPa.
Preferably, include nitrogen in wherein described high temperature anaerobic steam.It is highly preferred that nitrogen content is 10-80v.%, more It is preferred that 20-60v.%.
In the present invention, it is preferred to not carry out any pretreatment to rubbish.
For the present invention, compared with simple dry distilling of the prior art, the presence of nitrogen can avoid rubbish in carbonization During burn, make generation charcoal have higher calorific value.In addition, compared with pure steam gasification in prior art, The presence of nitrogen can also increase heating medium calorific value, improve the efficiency of heating surface so as to improve carbonization efficiency, while can also save Steam consumption, more importantly, by the addition of nitrogen, can be the catalysis bar needed for the offer of the catalysis upgrading of follow-up distillation Part, for example adjust needed for vapor partial pressure because too high vapour pressure can cause catalysis upgrading to be difficult to effectively carry out, nitrogen plus Enter the vapor partial pressure that can reduce in gas stream i.e. distillation.
The inventors discovered that, in existing waste steam treatment technology, often have ignored the composition for rubbish has choosing Steaming conditions are selected selecting property, the difference of rubbish composition is have ignored, is caused garbage treatment efficiency relatively low.The present inventor passes through Numerous studies, select different steaming conditions according to different rubbish compositions, obtain good steam treatment effect.Special Not, following high temperature distillation charing process condition is selected:(1) with the gross weight meter of rubbish, organic species in rubbish is constituted During weight % of content >=80, the temperature of high temperature anaerobic steam is 300-450 DEG C, preferably 300-400 DEG C;In high temperature anaerobic steam Nitrogen content is 10-30v.%, preferably 10-20v.%;The time of staying in high temperature distillation carbonizing apparatus is 8-12h;(2) When in rubbish composition with the gross weight meter of rubbish, during organic species 80 weight % of content < and preferably plastic, rubber class material During 10 weight % of content <, the temperature of high temperature anaerobic steam is 450 DEG C -600 DEG C, preferably 500 DEG C -550 DEG C;High temperature anaerobic steam In nitrogen content be 40-80v.%, preferably 60-80v.%;The time of staying in high temperature distillation carbonizing apparatus is 5-8h.
Further, for above-mentioned condition (1), when plastic, rubber class content of material >=10 weight %, high temperature anaerobic steams The temperature of vapour is 350-380 DEG C;Nitrogen content in high temperature anaerobic steam is 10-15v.%;In high temperature distillation carbonizing apparatus The time of staying be 8-10h;When plastic, rubber class content of material 10 weight % of <, the temperature of high temperature anaerobic steam is 300- 320℃;Nitrogen content in high temperature anaerobic steam is 25-30v.%;The time of staying in high temperature distillation carbonizing apparatus is 11- 14h.Research finds, high temperature distillation carbonization condition as selecting, and it is high temperature distillation carbonization due to plastic, rubber class material to be One of source of bio oil in journey, the composition such as the rubbish from cooking that compares and wood grass, which is very quick to steam distillation carbonization condition Sense, when its content is high, the temperature and water vapour that need application higher decompose which, but distillation carbonization time again can not mistake Long, otherwise it is easy to make the bio oil of generation resolve into micro-molecular gas, causes biological oil yield to reduce, and produce harmful by-product Thing.
When in rubbish, organic species content is higher, above-mentioned steaming conditions are particularly conducive to produce liquid combustible thing Generation;And organic species content relatively low when, be particularly conducive to the generation of charcoal class material.
For the present invention, the gas stream is preferably substantially free of two English.Because of the distillation that heats up under anaerobic state, institute So that the harmful substances such as two English will not be produced, can be with environment protection.This has very big excellent compared to common burning method Gesture.
Preferably, the high temperature anaerobic steam wherein used in high temperature distillation carbonizing apparatus is from high pressure through-flow steam oven.
10 weight %, more preferably less than preferably shorter than 5 weight %, 2 weight % are less than through oxygen content in the bio oil of upgrading. Further, it is more than 40MJ/kg through the higher calorific value of the bio oil of upgrading.Preferably, the pH through the bio oil of upgrading is 5-8. Preferably, 3.0wt.% is less than through the content of unsaturated phenol in the bio oil of upgrading.
Description of the drawings
Fig. 1 is the top view of the high temperature distillation carbonizing apparatus according to the present invention;
Fig. 2 is the SEM figures of catalyst obtained according to embodiments of the present invention 1;
Fig. 3 be using according to embodiments of the present invention 1 catalyst in bio oil upgrading each component content (GC-MS always from Subflow) variation with temperature figure.
Specific embodiment
With reference to following examples and comparative example, the present invention is described in further detail, but the embodiment party of the present invention Formula not limited to this.
Embodiment 1
Choosing and the house refuse of garbage compression transfer station being occupied from five tunnel of Haidian District, Beijing City, the composition of the rubbish is through inspection Survey as shown in table 1 below:
Table 1:Domestic waste is into being grouped into
High temperature distillation carbonization is carried out to above-mentioned rubbish by following steps:Rubbish is loaded rubbish feeding device;Make rubbish Feeding device passes through high temperature distillation carbonizing apparatus;Gas stream is taken out from high temperature distillation carbonizing apparatus top;Make the gas stream Pass through catalyst bed in a gaseous form;The effluent of self-catalysis agent in future bed is condensed and is separated, obtain liquid combustible thing and Water;Charcoal class material is obtained from the rubbish feeding device through high temperature distillation carbonizing apparatus.The high temperature distillation carbonizing apparatus passes through High temperature anaerobic steam is heated, and the temperature of high temperature anaerobic steam is 355 DEG C, and the nitrogen content in high temperature anaerobic steam is 12v.%, processed average time for 9.0 hours.In gas stream, combustible organic carries out upgrading, institute using hydrodeoxygenation process The catalyst for stating catalyst bed is Ni-Cu-Pd-Co2O3-Fe2O3The mol ratio of/HZSM-5, wherein Ni, Cu, Pd, Co, Fe is 2: 8:0.15:1.5:15, based on overall catalyst weight gauge, Ni-Cu-Pd-Co2O3-Fe2O3The content of catalytic active component is 5%, Hydrogenation upgrading condition is 300 DEG C, 3.0MPa hydrogen pressures, 3h.Coke is obtained by the method and the bio oil through upgrading.The life Oxygen content in thing oil is 4.1wt.%, is 43MJ/kg through the higher calorific value of the bio oil of upgrading, and catalyst life is for about 722h.
Comparative example 1
The comparative example and embodiment 1 differ only in bio oil upgrading using catalyst be conventional NiMo/Al2O3 Catalyst.Oxygen content in the bio oil through upgrading for obtaining is 19.6wt.%, through the higher calorific value of the bio oil of upgrading is 28MJ/kg, catalyst life are for about 120h.
The method of the present invention clearly can be seen that by above-described embodiment and comparative example and be obtained in that substantially preferably upgrading Effect.In addition, the bio oil of the inventive method upgrading, with relatively low oxygen content, so as to have higher calorific value, is hydrogenated with addition The catalyst life of upgrading is also greatly improved.
This written description discloses the present invention using example, including optimal mode, and also enables those skilled in the art Manufacture and using the present invention.The present invention can patentable scope be defined by the claims, and this area skill can be included Other examples that art personnel expect.If other examples this have structural elements not different from the literal language of claims Element, or if other examples this include the equivalent structure element with the literal language of claims without substantial differences, Then other examples this are intended within the scope of claims.In the case where inconsistent degree is not resulted in, by reference to To be incorporated herein in place of all references for referring to herein.

Claims (10)

1. a kind of catalyst for bio oil upgrading, the catalyst are the ferrum-based catalyst of silicate load.
2. catalyst according to claim 1, wherein described silicate are molecular sieve.
3. catalyst according to claim 2, wherein described molecular sieve are HZSM-5 molecular sieves.
4. application of the catalyst according to any one of claim 1-3 in bio oil upgrading.
5. application according to claim 4, the bio oil is from composting charing process.
6., according to the application of claim 4-5, wherein in grading process, the bio oil is with comprising bio oil and water vapour The form of gaseous stream carries out upgrading.
7. application according to claim 6, wherein described upgrading are hydrogenation upgrading.
8. application according to claim 6, is wherein less than 3.0wt.% through the content of unsaturated phenol in the bio oil of upgrading.
9. application according to claim 6, will isolate bio oil and water through upgrading wherein after upgrading from logistics.
10. application according to claim 6, wherein described separation are carried out by distillating method.
CN201611023688.0A 2016-11-22 2016-11-22 A kind of catalyst for bio oil upgrading Expired - Fee Related CN106492873B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611023688.0A CN106492873B (en) 2016-11-22 2016-11-22 A kind of catalyst for bio oil upgrading

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611023688.0A CN106492873B (en) 2016-11-22 2016-11-22 A kind of catalyst for bio oil upgrading

Publications (2)

Publication Number Publication Date
CN106492873A true CN106492873A (en) 2017-03-15
CN106492873B CN106492873B (en) 2019-03-08

Family

ID=58327238

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611023688.0A Expired - Fee Related CN106492873B (en) 2016-11-22 2016-11-22 A kind of catalyst for bio oil upgrading

Country Status (1)

Country Link
CN (1) CN106492873B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107325835A (en) * 2017-06-15 2017-11-07 上海交通大学 The method that hydro-thermal method converts grease or higher fatty acids is long chain alkane
CN113004953A (en) * 2021-03-16 2021-06-22 中国人民解放军空军勤务学院 Method for preparing biological aviation fuel by using coconut oil
CN113308265A (en) * 2020-02-26 2021-08-27 中国石油化工股份有限公司 Method for preparing biological crude oil by catalytic conversion method

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101787005A (en) * 2010-01-14 2010-07-28 浙江大学 Method for improving quality of biological oil through one-step hydroesterification of furfural and acetic acid in the presence of catalyst
CN102218324A (en) * 2011-04-19 2011-10-19 安徽理工大学 Catalyst for removing oxygen and improving quality of bio-oil and preparation method thereof
CN102994137A (en) * 2012-12-13 2013-03-27 青岛大学 Method for preparing algae material fuel by catalytic liquefying method
CN103343055A (en) * 2013-06-24 2013-10-09 合肥工业大学 Method for quality improvement of biological oil through catalytic esterification-deoxidize reforming in subcritical alcohol system
CN103949281A (en) * 2014-04-26 2014-07-30 东北农业大学 Preparation method of ultrasonic-assisted pyrolysis bio-oil modified MCM-41 molecular sieve loaded NiO catalyst as well as application thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101787005A (en) * 2010-01-14 2010-07-28 浙江大学 Method for improving quality of biological oil through one-step hydroesterification of furfural and acetic acid in the presence of catalyst
CN102218324A (en) * 2011-04-19 2011-10-19 安徽理工大学 Catalyst for removing oxygen and improving quality of bio-oil and preparation method thereof
CN102994137A (en) * 2012-12-13 2013-03-27 青岛大学 Method for preparing algae material fuel by catalytic liquefying method
CN103343055A (en) * 2013-06-24 2013-10-09 合肥工业大学 Method for quality improvement of biological oil through catalytic esterification-deoxidize reforming in subcritical alcohol system
CN103949281A (en) * 2014-04-26 2014-07-30 东北农业大学 Preparation method of ultrasonic-assisted pyrolysis bio-oil modified MCM-41 molecular sieve loaded NiO catalyst as well as application thereof

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107325835A (en) * 2017-06-15 2017-11-07 上海交通大学 The method that hydro-thermal method converts grease or higher fatty acids is long chain alkane
CN107325835B (en) * 2017-06-15 2020-04-28 上海交通大学 Method for converting grease or higher fatty acid into long-chain alkane by hydrothermal method
CN113308265A (en) * 2020-02-26 2021-08-27 中国石油化工股份有限公司 Method for preparing biological crude oil by catalytic conversion method
CN113004953A (en) * 2021-03-16 2021-06-22 中国人民解放军空军勤务学院 Method for preparing biological aviation fuel by using coconut oil
CN113004953B (en) * 2021-03-16 2022-05-20 中国人民解放军空军勤务学院 Method for preparing biological aviation fuel by using coconut oil

Also Published As

Publication number Publication date
CN106492873B (en) 2019-03-08

Similar Documents

Publication Publication Date Title
Zhang et al. A review of bio-oil upgrading by catalytic hydrotreatment: Advances, challenges, and prospects
Malins et al. Bio-oil from thermo-chemical hydro-liquefaction of wet sewage sludge
Yeh et al. Hydrothermal catalytic production of fuels and chemicals from aquatic biomass
CN106732502B (en) A kind of hydrogenation catalyst
Mahdi et al. Catalytic deoxygenation of palm oil and its residue in green diesel production: A current technological review
CN106492873B (en) A kind of catalyst for bio oil upgrading
Hai et al. Pyrolysis of date seeds loaded with layered double hydroxide: kinetics, thermodynamics, and pyrolytic gas properties
Galadima et al. Towards sustainable catalysts in hydrodeoxygenation of algae-derived oils: A critical review
Hosseini et al. Hydrothermal liquefaction of granular bacteria to high-quality bio-oil using Ni–Ce catalysts supported on functionalized activated carbon
CN106732704B (en) A kind of antigravity system reducing biomass char oil content in bio oil
Hosseinpour et al. Production of high‐quality bio‐product by pyrolysis of acid/metal modified chickpea husk
Gao et al. Hydrodeoxygenation of lignin biophenolics to cyclohexanes over sub-nanometric Ru multifunctional catalyst
Zhang et al. Upcycling waste polycarbonate plastics into jet fuels over NiCo/C by catalytic tandem hydropyrolysis/hydrodeoxygenation
Meng et al. In Situ Synergistic Catalysis Hydrothermal Liquefaction of Spirulina by CuO–CeO2 and Ni–Co to Improve Bio-oil Production
Xu et al. Catalytic pyrolysis of waste cooking oil for hydrogen-rich syngas production over bimetallic Fe-Ru/ZSM-5 catalyst
Morris Production of bio-oils via catalytic pyrolysis
KR101729322B1 (en) Activated charcoal catalyst using for enhancing chemical quality of biocrude oil and method for preparing biocrude oil enhanced chemical quality using the same
CN110898850B (en) Preparation and application method of catalyst for extracting wood vinegar and bio-oil
Oh et al. Pretreatment of bio-oil with ion exchange resin to improve fuel quality and reduce char during hydrodeoxygenation upgrading with Pt/C
CN106622353B (en) A kind of garbage disposal catalyst with superheated vapor stability
CN105602612B (en) Method for hydrofinishing biological crude oil by using high temperature gas cooled reactor
CN106381165B (en) A kind of combustible organic plus hydrogen method for upgrading
CN106495153A (en) The method of production material with carbon element
CN106622349B (en) Catalyst for the processing of high temperature garbage retort gas
Oyebanji et al. Box Behnken design application for optimization of bio-oil yield from catalytic pyrolysis of agro-residue

Legal Events

Date Code Title Description
C06 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
TR01 Transfer of patent right

Effective date of registration: 20201015

Address after: 102200 8222, floor 2, building 1, east of Gulou South Street, Chengbei street, Changping District, Beijing

Patentee after: Beijing union Green Technology Group Co.,Ltd.

Address before: 100190, room 9, No. 1708 West Fourth Ring Road, Haidian District, Beijing

Patentee before: New Austrian Ecological Environment Management Co.,Ltd.

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

Granted publication date: 20190308