WO2012071005A1 - A method of producing bio oil using ultra high temperature steam pyrolysis of carbonaceous solids - Google Patents
A method of producing bio oil using ultra high temperature steam pyrolysis of carbonaceous solids Download PDFInfo
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- WO2012071005A1 WO2012071005A1 PCT/SE2011/051406 SE2011051406W WO2012071005A1 WO 2012071005 A1 WO2012071005 A1 WO 2012071005A1 SE 2011051406 W SE2011051406 W SE 2011051406W WO 2012071005 A1 WO2012071005 A1 WO 2012071005A1
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- Prior art keywords
- pyrolysis
- oil
- reactor
- bio
- temperature steam
- Prior art date
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- 238000000034 method Methods 0.000 title claims abstract description 81
- 239000012075 bio-oil Substances 0.000 title claims abstract description 62
- 239000007787 solid Substances 0.000 title claims description 29
- 238000002352 steam pyrolysis Methods 0.000 title description 5
- 238000000197 pyrolysis Methods 0.000 claims abstract description 88
- 239000001257 hydrogen Substances 0.000 claims abstract description 35
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 35
- 239000002028 Biomass Substances 0.000 claims abstract description 31
- 239000002994 raw material Substances 0.000 claims abstract description 29
- 239000007789 gas Substances 0.000 claims description 41
- 239000007788 liquid Substances 0.000 claims description 29
- 238000001816 cooling Methods 0.000 claims description 19
- 238000006392 deoxygenation reaction Methods 0.000 claims description 15
- 238000010791 quenching Methods 0.000 claims description 14
- 230000000171 quenching effect Effects 0.000 claims description 13
- 239000002699 waste material Substances 0.000 claims description 9
- 239000000203 mixture Substances 0.000 claims description 5
- 238000009833 condensation Methods 0.000 claims description 2
- 230000005494 condensation Effects 0.000 claims description 2
- 238000011084 recovery Methods 0.000 claims description 2
- 239000011343 solid material Substances 0.000 claims description 2
- 230000008569 process Effects 0.000 abstract description 47
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 21
- 229910052760 oxygen Inorganic materials 0.000 abstract description 21
- 239000001301 oxygen Substances 0.000 abstract description 21
- 239000000463 material Substances 0.000 abstract description 14
- 238000004519 manufacturing process Methods 0.000 abstract description 11
- 238000005336 cracking Methods 0.000 abstract description 6
- 239000002910 solid waste Substances 0.000 abstract description 5
- 238000002407 reforming Methods 0.000 abstract description 4
- 239000000126 substance Substances 0.000 abstract description 4
- 238000010494 dissociation reaction Methods 0.000 abstract description 2
- 230000005593 dissociations Effects 0.000 abstract 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 13
- 239000000446 fuel Substances 0.000 description 13
- 238000010438 heat treatment Methods 0.000 description 9
- 229910001868 water Inorganic materials 0.000 description 9
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 8
- 239000003921 oil Substances 0.000 description 8
- 239000004033 plastic Substances 0.000 description 8
- 229920003023 plastic Polymers 0.000 description 8
- 238000002485 combustion reaction Methods 0.000 description 7
- 238000005984 hydrogenation reaction Methods 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 230000008901 benefit Effects 0.000 description 6
- 239000003546 flue gas Substances 0.000 description 6
- 241000894007 species Species 0.000 description 6
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 5
- 235000017491 Bambusa tulda Nutrition 0.000 description 5
- 241001330002 Bambuseae Species 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 5
- 241000196324 Embryophyta Species 0.000 description 5
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 5
- 239000011425 bamboo Substances 0.000 description 5
- 239000003054 catalyst Substances 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 5
- 239000003795 chemical substances by application Substances 0.000 description 5
- 239000010813 municipal solid waste Substances 0.000 description 5
- 238000011020 pilot scale process Methods 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- YZCKVEUIGOORGS-IGMARMGPSA-N Protium Chemical compound [1H] YZCKVEUIGOORGS-IGMARMGPSA-N 0.000 description 4
- 150000001875 compounds Chemical class 0.000 description 4
- 229930195733 hydrocarbon Natural products 0.000 description 4
- 150000002430 hydrocarbons Chemical class 0.000 description 4
- 239000004215 Carbon black (E152) Substances 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 3
- 239000002551 biofuel Substances 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 239000000571 coke Substances 0.000 description 3
- 238000006482 condensation reaction Methods 0.000 description 3
- 230000009849 deactivation Effects 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000005755 formation reaction Methods 0.000 description 3
- 239000000852 hydrogen donor Substances 0.000 description 3
- 230000001965 increasing effect Effects 0.000 description 3
- 239000002029 lignocellulosic biomass Substances 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 238000006213 oxygenation reaction Methods 0.000 description 3
- 238000009834 vaporization Methods 0.000 description 3
- 230000008016 vaporization Effects 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000009529 body temperature measurement Methods 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 238000004939 coking Methods 0.000 description 2
- 238000000921 elemental analysis Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 230000007935 neutral effect Effects 0.000 description 2
- 238000005070 sampling Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 239000013585 weight reducing agent Substances 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 229920002488 Hemicellulose Polymers 0.000 description 1
- QJGQUHMNIGDVPM-BJUDXGSMSA-N Nitrogen-13 Chemical compound [13N] QJGQUHMNIGDVPM-BJUDXGSMSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 150000001299 aldehydes Chemical class 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- 230000003851 biochemical process Effects 0.000 description 1
- 239000003225 biodiesel Substances 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 239000003575 carbonaceous material Substances 0.000 description 1
- 150000001735 carboxylic acids Chemical class 0.000 description 1
- 238000004523 catalytic cracking Methods 0.000 description 1
- 238000004517 catalytic hydrocracking Methods 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 239000013626 chemical specie Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 125000000753 cycloalkyl group Chemical group 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 208000018459 dissociative disease Diseases 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000010892 electric spark Methods 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 125000000524 functional group Chemical class 0.000 description 1
- ZZUFCTLCJUWOSV-UHFFFAOYSA-N furosemide Chemical compound C1=C(Cl)C(S(=O)(=O)N)=CC(C(O)=O)=C1NCC1=CC=CO1 ZZUFCTLCJUWOSV-UHFFFAOYSA-N 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 230000020169 heat generation Effects 0.000 description 1
- 238000009616 inductively coupled plasma Methods 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 150000002605 large molecules Chemical class 0.000 description 1
- 229920005610 lignin Polymers 0.000 description 1
- 239000012978 lignocellulosic material Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 238000006116 polymerization reaction Methods 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000012265 solid product Substances 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 238000001991 steam methane reforming Methods 0.000 description 1
- 238000000629 steam reforming Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- 238000004227 thermal cracking Methods 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 230000001131 transforming effect Effects 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B49/00—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
- C10B49/02—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with hot gases or vapours, e.g. hot gases obtained by partial combustion of the charge
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
- C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
- C10B53/02—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10C—WORKING-UP PITCH, ASPHALT, BITUMEN, TAR; PYROLIGNEOUS ACID
- C10C5/00—Production of pyroligneous acid distillation of wood, dry distillation of organic waste
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
- C10G1/002—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal in combination with oil conversion- or refining processes
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
- C10G1/02—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal by distillation
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G3/00—Production of liquid hydrocarbon mixtures from oxygen-containing organic materials, e.g. fatty oils, fatty acids
- C10G3/50—Production of liquid hydrocarbon mixtures from oxygen-containing organic materials, e.g. fatty oils, fatty acids in the presence of hydrogen, hydrogen donors or hydrogen generating compounds
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
- C10G2300/10—Feedstock materials
- C10G2300/1003—Waste materials
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
- C10G2300/10—Feedstock materials
- C10G2300/1011—Biomass
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
- C10G2300/00—Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
- C10G2300/40—Characteristics of the process deviating from typical ways of processing
- C10G2300/4006—Temperature
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P30/00—Technologies relating to oil refining and petrochemical industry
- Y02P30/20—Technologies relating to oil refining and petrochemical industry using bio-feedstock
Definitions
- the present invention generally relates to the exploitation of carbonaceous, solid waste materials, and biomass, especially lignocellulosic materials for bio-oil production, and in particular to an advanced one step process that can produce upgraded bio-oil directly from solid waste materials or biomass by hydrodeoxygenation (HDO) using high-temperature steam, as well as an arrangement for carrying out the inventive process.
- HDO hydrodeoxygenation
- Biomass is a renewable energy source with increasing potential in the worldwide energy market, and its net carbon dioxide emissions are essentially neutral, thus not contributing to the greenhouse effect. Moreover, its very low nitrogen (N) and sulfur (S) contents add to the environmental friendly character of such a material.
- Municipal solid wastes also to a large extent comprises biomass and offer increased sustained potential for biofuel production, with cleaner environment.
- the plastics from municipal solid wastes also offer clean biofuel production with characteristics similar to that of biodiesel liquids.
- biomass apart from its neutral CO2 net characteristic, is that it can be converted to liquid, solid, or gaseous fuels, unlike other renewable sources of energy (e.g. wind, and solar energy), which only give heat and power.
- renewable sources of energy e.g. wind, and solar energy
- the municipal solid wastes that are also biomass can be converted to liquid fuels for use in propulsion and power systems.
- the dumping of plastics in landfill causes environmental issues, since the plastics are not biodegradable.
- the energy content in plastics is much higher than in biomass materials, so that its fuel reforming would offer benefits of negative cost fuels from such wastes, improved environment, and a permanent solution to the plastic wastes.
- biomass, solid wastes and plastics can be considered as a renewable re- source which could be directly transformed into liquid fuel and value added products and chemicals.
- thermochemical and bio-chemical processes The research in the area of transforming biomass has mostly focused on two aspects of thermochemical and bio-chemical processes.
- Biomass pyrolysis has at- tracted the highest interest amongst the thermochemical conversion technologies as it offers renewable liquid, gaseous and solid products converted by optimized technology conditions.
- Fast pyrolysis of biomass is one way to generate liquid from biomass. This is the most intensively investigated pyrolysis process at present. The key issues in order to obtain as much liquid as possible are rapid heating and rapid quenching. External heat is generally provided by sand in fluidized-bed reactors, or by a hot wall, such as in ablative (vortex and rotating blade) reactors. The main heat transfer modes are conduction and convection. Fast pyrolysis has been developed relatively recently. Intensive studies were carried out in 70s. Presently, many laboratories around the world are trying to commercialize "fast wood pyrolysis" to liquid.
- Demonstration plants include 400 kg/h at Dynamotive with fluidized bed reactor, 1 ,000 kg/h CFB at Red Arrow, and 20 kg/h at VTT. 120 kg/h of rotating cone reactor at BTG, (Netherlands), 3,500 kg/h at Pyrovac with a vacuum reactor, 350 kg/h at For- turn, Finland with an ablative reactor, and 200 kg/h at Mississippi State University, USA with an auger reactor.
- bio-oil directly derived from these traditional processes, is usually of high viscosity and exhibits a high content of oxygenated components, a low stability and a low heat value, and thus further processing and upgrading of the bio-oil is required.
- the oxygenated compounds present in raw bio-oil impart a number of un- wanted characteristics to the bio-oil, such as thermal instability (reflected in increasing viscosity upon storage of the bio-oil), corrosiveness and low heating value.
- This instability is associated with the presence of reactive chemical species, mainly aldehydes, ketones, carboxylic acids, alkenes and guaiacol-type molecules.
- reactive chemical species mainly aldehydes, ketones, carboxylic acids, alkenes and guaiacol-type molecules.
- condensation reactions involving the above mentioned functional groups result in formation of heavier compounds due to polymerization reactions.
- Upgrading biomass-derived oils to hydrocarbon fuels requires oxygen removal and molecular weight reduction. This requires that hydrogen is added in the process to increase the H/ C ratio of the product and to remove excess oxygen as water.
- the first comprises bio-oil cracking at atmospheric pressure, resulting in simultaneous dehydra- tiondecarboxylation.
- the second method for bio-oil upgrading utilizes typical hydrotreating conditions, i.e., high hydrogen pressures for the hydrogenation of unsaturated groups (with elimination of oxygen as water) and hydrogenation-hydrocracking of large mole- cules.
- hydrotreating is extremely effective, techno-economic analyses reveal its economics to be unfavorable for the production of the fuel-type products it affords.
- Hydrogen is typically derived from steam methane reforming, which is dependent on methane, and is therefore not normally considered a renewable source.
- Alternative methods of hydrogen production include the use of water electrolysis. The prior art methods of producing hydrogen are relatively costly.
- HDO hydrodeoxygenation
- the inventive method is a fast pyrolysis process for the production of bio-oil from a carbonaceous, solid raw material selected from waste materials and biomass materials, or a mixture thereof, and especially lignocellulosic raw materials.
- the method uses high-temperature steam to pyrolyse the raw material. By virtue of the presence of high-temperature steam during the pyrolysis, deoxygenation of oxygenated spe- cies in the pyrolysis gas will also be accomplished at the same time.
- upgraded bio-oil can be produced in a one-step process.
- the present inventors have found that, when high-temperature steam is used for pyrolysis of a lignocellulosic raw material, the degree of oxygenation in the resulting pyrolysis gases will be reduced. As alluded to in the article by Kantarelis et al.
- hydrogen may be transferred to the oxygenated or unsaturated molecules, and this generally enhances the quality of the resulting bio-oil.
- the present invention as described herein has been focused on using lignocellulosic raw materials, the present inventors also believe that the inventive method could be used for converting carbonaceous solid waste materials and biomass materials in general, such as municipal solid waste, waste plastics, waste tyres, and biomass, such as e.g. lignocellulosic biomass.
- the oxygen content of waste plastics and waste tyres is likely to be comparatively low in general, and therefore, when such materials are being used as the sole raw material for the process, the deoxy- genation capacity of the inventive process will not be taken full advantage of. Accordingly, it is preferred that the raw material, or mixture of raw materials, for the process contains a substantial amount of oxygen containing compounds.
- Municipal solid waste and / or biomass is used as the raw material in the inventive process, and more preferably biomass, especially lignocellulosic biomass.
- the invention relates to a method of producing bio-oil 120 from a carbonaceous, solid raw material 40 selected from waste materials and biomass, and mixtures thereof, which method in its most generic embodiment comprises the steps of: (a) providing a carbonaceous, solid raw material 40; (b) subjecting the carbonaceous, solid raw material to conditions effective for accomplishing fast pyrolysis of said carbonaceous, solid raw ma- terial; (c) subjecting the oxygenates formed in step (b) to conditions effective for accomplishing deoxygenation of said oxygenates; and (d) cooling the components 60 formed in step (c), in order to obtain liquid bio-oil 120, wherein steps (b) and (c) are accomplished by means of subjecting the carbonaceous, solid raw material to high- temperature steam 28 at a temperature within the interval of 400-700°C.
- the resulting bio-oil obtained upon quenching will be upgraded in respect of both hydrogen content, and also in respect oxygen content, i.e. the oxygen content will be low.
- steps (b) and (c), i.e. the pyrolysis and the deoxygenation, respectively, can be carried out in the same reactor 30.
- steps (b) and (c) can be combined into one step, wherein the raw material is subjected to preheated high-temperature steam.
- the char produced from the inventive process using high- temperature steam has been found to exhibit a higher surface area and higher carbon content, than char obtained from conventional pyrolysis.
- the char produced by the inventive process can therefore be used as e.g. an activated carbon precursor.
- any co-produced synthesis gas during the process will not be diluted, as opposed to when e.g. N2, or another inert gaseous component is being used. According to the claimed process, only steam is required to be added.
- the hydrogen enriched gas that is produced can thus be utilized for heat generation for providing the necessary high-temperature steam of the inventive process, as well as raw material for chemical synthesis.
- the bio-oil of the present invention generally comprises products containing low oxygen to carbon ratio (0:C) which is essential for a good quality bio-oil. This will enhance the production, as well as the use of bio-oil as transport fuel substitute or/ and chemicals.
- the present inventors have found the resulting bio-oil obtained by means of the method to have a reduced content of soot, a reduced viscosity, enhanced storage- life, and a lighter colour, than conventionally obtained bio-oil. Accordingly, as opposed to the prior art pyrolysis oil, which is usually black and opaque, the bio-oil of the invention is typically yellow to brown in colour, and essentially transparent.
- step (c) of the above generic embodiment of the method can be substantially enhanced by providing additional hydrogen radicals (H*) to the process, which radicals can be readily generated, using electrical means 50, from the high-temperature steam present in the process, that is in steps (b) and (c).
- H* hydrogen radicals
- H2O water molecules
- H* and OH* radicals
- H* and OH* radicals
- HDO hydrode- oxygenation
- the high-temperature steam consequently serves the dual purposes of both constituting a heat carrying agent, which supplies the major part of the necessary heat for effecting pyrolysis, and also constituting a source of hydrogen radicals, thus also supplying a reactive agent (H*) that will serve to deoxy- genate oxygen containing species in the pyrolysis gas, whereby the bio-oil, obtained upon quenching, will be upgraded in this respect and exhibit a low oxygen content.
- a heat carrying agent which supplies the major part of the necessary heat for effecting pyrolysis
- a source of hydrogen radicals thus also supplying a reactive agent (H*) that will serve to deoxy- genate oxygen containing species in the pyrolysis gas, whereby the bio-oil, obtained upon quenching, will be upgraded in this respect and exhibit a low oxygen content.
- additional hydrogen radicals are being generated and supplied to the method.
- the additional hydrogen radicals are being formed from the high-temperature steam in using electrical means.
- Oxygenates formed in pyrolysis step (b) are then brought into contact with the hydrogen radicals thus formed.
- deoxygenation of oxygenates contained in the pyrolysis gas will be enhanced, and the quality of the resulting bio-oil further improved.
- the use of a hydrogen radical generator will also serve to offer effective means of controlling the process, in terms of desired extent of hydrogenation and deoxygenation.
- the present invention relates to a corresponding arrangement for carrying out the above preferred inventive method comprising: a pyrolysis reactor 30 with the capability of withstanding temperatures in the range of 400-700°C, which reactor exhibits an inlet for a carbonaceous, solid raw material 40, and an inlet for high-temperature steam 28 of a temperature within the interval of 400- 700°C; and quenching means 100 for cooling the pyrolysis gas 60 obtained in the pyrolysis reactor 30, wherein the reactor further comprises electrical means 50 for producing hydrogen radicals (H*) from the high-temperature steam within the reactor.
- H* hydrogen radicals
- the arrangement also comprises separation means 70, such as e.g. a cyclone, for removing char and solid residues from the pyrolysis gas before quenching.
- separation means 70 such as e.g. a cyclone, for removing char and solid residues from the pyrolysis gas before quenching.
- the quenching means 100 is also provided with electrical means 50 for producing hydrogen radicals (H*) from the high-temperature steam within the quenching means.
- an arrangement for carrying out the above generic inventive method comprises: a pyrolysis reactor 30 with the capability of withstanding temperatures in the range of 400-700°C, which reactor exhibits an inlet for a car- bonaceous, solid raw material 40, and an inlet for high-temperature steam 28 of a temperature within the interval of 400-700°C; and quenching means 100 for cooling the pyrolysis gas obtained in the pyrolysis reactor 30, wherein the arrangement further comprises separation means 70 for removing char and solid residues 80 from the pyrolysis gas 60 before quenching, so as to obtain clean pyrolysis gas 90, which then can be quenched in cooler 100 so as to form bio-oil 120.
- Another objective is the online reforming of complex long chain hydrocarbons and cyclic hydrocarbons, formed from the carbonaceous, solid raw material fed into the process upon pyrolysis thereof, to enhance the hydrogenation of the produced bio- oil.
- biomass undergoes pyrolysis producing liquid oil, value added products and gaseous fuel products.
- liquid oil' as used herein means a liquid which is obtained upon quenching of the pyrolysis gases, and which is in a liquid state at room temperature.
- liq- uid oil, bio-oil and pyrolysis liquid have been used interchangeably herein.
- Figure 1 shows a general system flow diagram, wherein reference numeral 28 denotes a high-temperature steam inlet, 30 denotes a pyrolysis reactor, 40 carbona- ceous feeding, 50 hydrogen radical generators, 60 pyrolysis gas generated from pyrolysis reactor, 70 a cyclone separator, 80 char and solid residues, 90 clean pyrolysis gas, 100 a cooler, 1 10 syngas obtained from the process, and 120 denotes bio- oil obtained from the inventive process.
- Figure 2 shows a pilot batch plant, which was used for carrying out the inventive method in batch mode operation on a pilot scale, wherein 1 -4 denotes gas nozzles, 5 air nozzle, 6 methane nozzle, 7 gas burner, 8 combustion chamber, 9 ceramic honeycomb, 10 cooling chamber, 1 1 lid, 12 online gravimetric measurement, 13 cooling nitrogen nozzle, 14 perforated basket with sample, 15 flue gases, 16 sam- pling line, 17 gas washing bottle for liquid collection, 18 reaction chamber, 19 window, 20 thermocouple for steam temperature measurement, 21 thermocouple for sample temperature measurement, 22 cooling bath of -15°C to - 10°C, 23-26 cooling water, and 27 denotes a gas chromatograph.
- the pilot batch plant is not an embodiment of the arrangement of the invention.
- the inventive system includes a biomass pyrolysis reactor 30 working in the temperature range of 400°C to 700°C, into which reactor high-temperature preheated steam of a temperature within the range of 400°C to 700°C is injected.
- the stream is not only acting as a heating agent supplying the major part of the heat necessary for the pyrolysis, but also acting as a hydrogen donor, providing reactive hydrogen which will react with oxygenates in the pyrolysis gas, and thereby reduce the oxygen: carbon in order to get rid of oxygen.
- the preferred working temperature range of the pyrolysis reactor, and also of the high-temperature steam being fed into the reactor, is within the interval of about 440°C to 600°C.
- the heat required for the pyrolysis is mainly provided by the high-temperature steam entering the reactor. However, additionally heating will typically be required in order to maintain the temperature within the pyrolysis reactor within the range of 400-700°C.
- the additional heat can be provided by electrical heating of the reac- tor, and/ or by means of hot flue gases being passed into the pyrolysis reactor from combustion outside the reactor, such as e.g. from upstream generation of high- temperature steam. Such flue gases could enter the pyrolysis reactor together with the high-temperature steam, or via a separate inlet. Accordingly, the pyrolysis reactor may be provided with means for electrical heating thereof and / or an inlet for hot flue gases.
- the pyrolysis reactor uses a fixed or fluidized bed, preferably a fluidized bed, to which the carbonaceous raw material is being fed.
- the pyrolysis reactor is preferably operating at essentially atmospheric pressure, since otherwise the bio-oil yield will decrease.
- the high- temperature steam is fed into the pyrolysis reactor preferably at about atmospheric pressure.
- the pyrolysis reactor is provided with electrical means for generating hydrogen radicals from the high-temperature steam in the pyrolysis reactor. Hydrogen radicals can e.g. be generated by means of electrical discharge, such as electrodes, or plasma.
- the electrical discharge is preferably operating continuously during the pyrolysis.
- the electrical means discharge or plasma
- the electrical means is preferably located in the freeboard of the bed.
- the bio-oil produced during the pyrolysis process is simultaneously cracked and reformed in the presence of steam to produce 3 ⁇ 4.
- Produced hydrogen can take part in hydrogenation reactions; in addition hydrogen radicals from the highly superheated steam, and/or from the electric spark, or plasma, can also take part in the HDO of the of the oxygenated species contained in the pyroly- sis gas, so as to produce an upgraded bio-oil.
- the hydrogen radicals are very reactive during thermal cracking.
- Hydrogen radicals are hydrogen donors enhancing the online upgrading of the produced bio-oil.
- the above mentioned can be schematically depicted by the following scheme:
- the co-produced gas is a hydrogen rich gas and therefore a valuable gas product.
- the solid residue produced from the process exhibits enhanced surface characteristics that can enhance the exploitation of the material.
- the pyrolysis vapors leaving the reactor are being passed through a tube and are rapidly quenched. With reference to the pilot plant illustrated in Figure 2, this can be accomplished using gas washing bottles at temperatures of - 10°C down to - 15°C, and a cooling bath. In large scale plants, the cooling temperature will typically be atmospheric or ambient. Condensable molecules are then obtained as a liquid, i.e. as bio-oil.
- a process for converting carbonaceous materials to liquid comprises the following steps. Feeding preheated high- temperature steam 28 of a temperature within the range of 400°C to 700°C, which can be generated by a regenerative system, an electrical heater, a boiler, or from combustion of hydrogen and oxygen. Feeding the carbonaceous, solid material 40 into pyrolysis reactor 30.
- the reactor 30 is operating in the temperature of 400°C to 700°C.
- the temperature of reactor 30 is maintained by an electric heater (not shown), or by hot flue gases from combustion of e.g.
- a hydrogen radical generator 50 is installed in the reactor 30. This generator produces hydrogen radicals (H * ), which are used as a hydrogen donor for the deoxygenation process of the pyrolysis gas.
- the stream of pyrolysis gas 60 generated from the pyrolysis reactor 30 passes through a cyclone separator 70.
- solid residues 80 can be separated from the pyrolysis gas stream 60.
- a clean pyrolysis gas stream 90 exiting cyclone 70 flows into a cooler 100. Here, most of the gas is cooled to produce a pyrolysis liquid (i.e. bio-oil) 120.
- a hydrogen radical generator 50 is also installed in the cooler 100 in order to provide hydrogen radicals also at this loca- tion, enabling additional deoxygenation reaction of the gaseous oxygenates and hy- drogenation reaction of gaseous unsaturated compounds before being converted into a liquid state.
- the pilot scale apparatus is based on a universal batch reactor, which reactor has been developed for a different purpose and has been described in more detail by Anna Ponzio, Sylvester Kalizs, Juliette Promelle, Wlodzimierz Blasiak, Susumo Mochida, Combustion of wood pellets in a high temperature and oxygen diluted environment, Proceedings from 6 th Hi- TACG conference 2005 , Essen 2005.
- the pilot scale plant shown in Figure 2 is not an arrangement according to the invention.
- the experimental pilot scale rig shown in Figure 2 consists of a horizontal combustion chamber with an inner diameter about 0. 1 m.
- High-temperature steam was obtained as follows. Methane and air were fed via nozzles 5 and 6 to the gas burner 7. As the fuel burns in the combustion chamber 8 the hot flue gases will heat the ceramic honeycomb 9 and flow through the second part of the reactor 18 and towards the reactor's outlet 15. The rig is run in heating mode until the desired temperature of the honeycomb is reached. Once the proper temperature is reached, the methane feed is shut off and the experimental stage started.
- the proper feed gas (in this case N2) is set by adjusting the flow of steam and the resulting heating agent is fed through feed gas nozzles 1-4 and is heated by the hot honeycomb 9.
- the heated agent temperature is measured by a thermocouple 20.
- a portion of a feedstock is attached to a piston as a thin bed in a basket 14 fabricated by metal net for this purpose.
- the lid 11 with the piston and the feedstock sample is attached to the rig, with the feedstock sample in a small cooling chamber 10 where it is cooled by nitrogen 13.
- the experiment starts when the sample on the piston is pushed down into the reactor chamber 18 from above. Once the sample is in the chamber, the sample is visible through glass window 19.
- the temperature of the sample is measured by a thermocouple 21. Thereafter, the basket is lifted from the chamber to the cooling chamber 10 in order to quench the reactions through cooling with nitrogen.
- the pyrolysis vapors leaving the reactor are passed a sampling line 16 and they are rapidly quenched by gas washing bottles 17 to temperatures of - 10°C down to - 15°C, using a cooling bath 22. Condensable molecules are obtained as a liquid.
- the gases are driven to GC analyzer 27.
- bamboo has been tested in above facility.
- the particle size of the bamboo was about 200-500 ⁇ .
- the elemental analysis was performed using a Vario Micro Elemental Analysis instrument.
- the alkali content and other metals that can be found in the ash of the material were analyzed using a PE5300DV inductively coupled plasma spectrometer. Table 1 Analysis of the raw material
- the water content in the resulting liquids were around 30% and the liquids obtained were fully miscible in water.
- the bio-oils obtained were transparent, brown liquids. Elemental composition of bio-oil obtained from steam pyrolysis at 797 K (523.85°C)
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Abstract
An advanced process concept for upgraded bio-oil production from carbonaceous, solid waste materials and biomass materials, especially a lignocellulosic raw material, in a one step method is proposed. Introduction of high-temperature steam in biomass pyrolysis process results in a low oxygen content upgraded bio-oil with an O/C ratio less than 0.2. The introduction of high-temperature steam allows the reforming and cracking of heavy bio-oil molecules to lower molecular weight sub- stances while the hydrogen radicals that are present due to steam dissociation re- actions are taking part in the hydrodeoxygenation (HDO) of the primary oxygenated species resulting from the pyrolysis.
Description
A METHOD OF PRODUCING BIO OIL USING ULTRA HIGH TEMPERATURE
STEAM PYROLYSIS OF CARBONACEOUS SOLIDS
FIELD OF THE INVENTION
The present invention generally relates to the exploitation of carbonaceous, solid waste materials, and biomass, especially lignocellulosic materials for bio-oil production, and in particular to an advanced one step process that can produce upgraded bio-oil directly from solid waste materials or biomass by hydrodeoxygenation (HDO) using high-temperature steam, as well as an arrangement for carrying out the inventive process.
DESCRIPTION OF THE PRIOR ART
Biomass is a renewable energy source with increasing potential in the worldwide energy market, and its net carbon dioxide emissions are essentially neutral, thus not contributing to the greenhouse effect. Moreover, its very low nitrogen (N) and sulfur (S) contents add to the environmental friendly character of such a material.
Municipal solid wastes also to a large extent comprises biomass and offer increased sustained potential for biofuel production, with cleaner environment. The plastics from municipal solid wastes also offer clean biofuel production with characteristics similar to that of biodiesel liquids.
The most important advantage of biomass, apart from its neutral CO2 net characteristic, is that it can be converted to liquid, solid, or gaseous fuels, unlike other renewable sources of energy (e.g. wind, and solar energy), which only give heat and power.
Similarly, the municipal solid wastes that are also biomass can be converted to liquid fuels for use in propulsion and power systems. The dumping of plastics in landfill causes environmental issues, since the plastics are not biodegradable. The energy content in plastics is much higher than in biomass materials, so that its fuel
reforming would offer benefits of negative cost fuels from such wastes, improved environment, and a permanent solution to the plastic wastes.
Therefore, biomass, solid wastes and plastics can be considered as a renewable re- source which could be directly transformed into liquid fuel and value added products and chemicals.
The research in the area of transforming biomass has mostly focused on two aspects of thermochemical and bio-chemical processes. Biomass pyrolysis has at- tracted the highest interest amongst the thermochemical conversion technologies as it offers renewable liquid, gaseous and solid products converted by optimized technology conditions.
There are basically two methods being used to produce oil from biomass: high pres- sure liquefaction (typically hydro thermal for biomass), and atmospheric pressure fast pyrolysis. Available biomass pyrolysis technology for bioliquid production is to convert organics to solid, liquid and gas by heating in the absence of oxygen.
Fast pyrolysis of biomass is one way to generate liquid from biomass. This is the most intensively investigated pyrolysis process at present. The key issues in order to obtain as much liquid as possible are rapid heating and rapid quenching. External heat is generally provided by sand in fluidized-bed reactors, or by a hot wall, such as in ablative (vortex and rotating blade) reactors. The main heat transfer modes are conduction and convection. Fast pyrolysis has been developed relatively recently. Intensive studies were carried out in 70s. Presently, many laboratories around the world are trying to commercialize "fast wood pyrolysis" to liquid. Demonstration plants include 400 kg/h at Dynamotive with fluidized bed reactor, 1 ,000 kg/h CFB at Red Arrow, and 20 kg/h at VTT. 120 kg/h of rotating cone reactor at BTG, (Netherlands), 3,500 kg/h at Pyrovac with a vacuum reactor, 350 kg/h at For- turn, Finland with an ablative reactor, and 200 kg/h at Mississippi State University, USA with an auger reactor.
However, bio-oil, directly derived from these traditional processes, is usually of high viscosity and exhibits a high content of oxygenated components, a low stability and a low heat value, and thus further processing and upgrading of the bio-oil is required. The oxygenated compounds present in raw bio-oil impart a number of un- wanted characteristics to the bio-oil, such as thermal instability (reflected in increasing viscosity upon storage of the bio-oil), corrosiveness and low heating value. This instability is associated with the presence of reactive chemical species, mainly aldehydes, ketones, carboxylic acids, alkenes and guaiacol-type molecules. During prolonged storage, condensation reactions involving the above mentioned functional groups result in formation of heavier compounds due to polymerization reactions.
From all the above it can be understood that upgrading biomass-derived oils to hydrocarbon fuels requires oxygen removal and water content and molecular weight reduction. In order to improve quality of the thus obtained bio-oil usually processes such as cracking, hydrogenation, and steam reforming are involved. An upgrading process of this kind of oil is needed. The concept of achieving a conversion of ligno- cellulosic biomass into liquid biofuels that are physically and chemically compatible with petroleum-based hydrocarbon fuels can be expressed by the formula:
Biomass -» Volatile (CxHyOz)+ Char (C) CxH O > -CH2 -
Upgrading biomass-derived oils to hydrocarbon fuels requires oxygen removal and molecular weight reduction. This requires that hydrogen is added in the process to increase the H/ C ratio of the product and to remove excess oxygen as water.
To date, two main deoxygenation methods have been investigated. The first comprises bio-oil cracking at atmospheric pressure, resulting in simultaneous dehydra- tiondecarboxylation.
Before cracking, however, the bio-oil must be vaporized. Such vaporization process is energy intensive, and causes undesired coke formation reactions and condensation reactions. If catalytic cracking is being employed severe coking and therefore deactivation of the catalysts will put a limitation to their application.
The second method for bio-oil upgrading utilizes typical hydrotreating conditions, i.e., high hydrogen pressures for the hydrogenation of unsaturated groups (with elimination of oxygen as water) and hydrogenation-hydrocracking of large mole- cules. Although hydrotreating is extremely effective, techno-economic analyses reveal its economics to be unfavorable for the production of the fuel-type products it affords. Hydrogen is typically derived from steam methane reforming, which is dependent on methane, and is therefore not normally considered a renewable source. Alternative methods of hydrogen production include the use of water electrolysis. The prior art methods of producing hydrogen are relatively costly.
The most suitable and effective method for upgrading bio-oil is hydrodeoxygenation (HDO). During HDO, oxygen in the feed is converted to ¾0 which is environmentally benign.
The main problems with the upgrading methods described above is the coke deposition, and, as a result, catalyst deactivation, even though several catalysts have been tested, as well as the hydrogen availability and complexity of high pressure processes.
Moreover, the above prior art bio-oil upgrading processes are being carried out offline from the pyrolysis, using pyrolysis derived bio-oil as raw material. Accordingly, it would be desirable to provide a process enabling on-line bio-oil upgrading.
A method solving the above problems has recently been disclosed by Kantarelis, E.; Liu, J.; Yang, W.; and Blasiak, W., Sustainable Valorization of Bamboo via High- Temperature Steam Pyrolysis for Energy Production and Added Value Materials, Energy Fuels 2010 (DOI: 10. 1021 /efl00875g published on 1 November 2010, accessible from http: / /pubs. acs.org) , the contents of which is incorporated herein in its entirety by reference.
The inventive method is a fast pyrolysis process for the production of bio-oil from a carbonaceous, solid raw material selected from waste materials and biomass materials, or a mixture thereof, and especially lignocellulosic raw materials. The method uses high-temperature steam to pyrolyse the raw material. By virtue of the presence of high-temperature steam during the pyrolysis, deoxygenation of oxygenated spe-
cies in the pyrolysis gas will also be accomplished at the same time.
It has recently been found by same inventors, that the deoxygenation can be further enhanced by means of providing additional hydrogen radicals (H*) to the process, which radicals can be readily generated, using electrical means, from the high- temperature steam.
According to the invention, upgraded bio-oil can be produced in a one-step process. SUMMARY OF THE INVENTION
The present inventors have found that, when high-temperature steam is used for pyrolysis of a lignocellulosic raw material, the degree of oxygenation in the resulting pyrolysis gases will be reduced. As alluded to in the article by Kantarelis et al.
above, hydrogen may be transferred to the oxygenated or unsaturated molecules, and this generally enhances the quality of the resulting bio-oil.
While the present invention as described herein has been focused on using lignocellulosic raw materials, the present inventors also believe that the inventive method could be used for converting carbonaceous solid waste materials and biomass materials in general, such as municipal solid waste, waste plastics, waste tyres, and biomass, such as e.g. lignocellulosic biomass. The oxygen content of waste plastics and waste tyres is likely to be comparatively low in general, and therefore, when such materials are being used as the sole raw material for the process, the deoxy- genation capacity of the inventive process will not be taken full advantage of. Accordingly, it is preferred that the raw material, or mixture of raw materials, for the process contains a substantial amount of oxygen containing compounds. Preferably, municipal solid waste and / or biomass is used as the raw material in the inventive process, and more preferably biomass, especially lignocellulosic biomass.
Accordingly, in a first aspect, and with reference to Figure 1 , the invention relates to a method of producing bio-oil 120 from a carbonaceous, solid raw material 40 selected from waste materials and biomass, and mixtures thereof, which method in its most generic embodiment comprises the steps of: (a) providing a carbonaceous, solid raw material 40; (b) subjecting the carbonaceous, solid raw material to conditions effective for accomplishing fast pyrolysis of said carbonaceous, solid raw ma-
terial; (c) subjecting the oxygenates formed in step (b) to conditions effective for accomplishing deoxygenation of said oxygenates; and (d) cooling the components 60 formed in step (c), in order to obtain liquid bio-oil 120, wherein steps (b) and (c) are accomplished by means of subjecting the carbonaceous, solid raw material to high- temperature steam 28 at a temperature within the interval of 400-700°C.
By means of the method, the resulting bio-oil obtained upon quenching will be upgraded in respect of both hydrogen content, and also in respect oxygen content, i.e. the oxygen content will be low.
In the inventive method, steps (b) and (c), i.e. the pyrolysis and the deoxygenation, respectively, can be carried out in the same reactor 30.
Also, steps (b) and (c) can be combined into one step, wherein the raw material is subjected to preheated high-temperature steam.
As opposed to the prior art, no intervening condensation or recovery step between the pyrolysis step and the deoxygenation step is required, and steps (b) and (c) can be combined into one step. Thus, upgraded, low oxygen content, hydrodeoxygen- ated bio-oil can be obtained in merely one step, in addition to the quenching step, that is.
Accordingly, any energy intensive vaporization of raw bio-oil, such as in the prior art off-line cracking processes used for upgrading the bio-oil, is avoided by means of the inventive in-line upgrading process.
Also, undesired coke formation reactions and condensation reactions associated with the prior art vaporization process are avoided by means of the invention. In the inventive process, no catalyst is required, and therefore any problem of deactivation of the catalyst due to e.g. coking is avoided.
Additionally, the use of high-temperature steam in the pyrolysis has been found to reduce the yield of char. The char produced from the inventive process using high- temperature steam has been found to exhibit a higher surface area and higher carbon content, than char obtained from conventional pyrolysis. The char produced by
the inventive process can therefore be used as e.g. an activated carbon precursor.
Also, by using steam, any co-produced synthesis gas during the process will not be diluted, as opposed to when e.g. N2, or another inert gaseous component is being used. According to the claimed process, only steam is required to be added. The hydrogen enriched gas that is produced can thus be utilized for heat generation for providing the necessary high-temperature steam of the inventive process, as well as raw material for chemical synthesis. The bio-oil of the present invention generally comprises products containing low oxygen to carbon ratio (0:C) which is essential for a good quality bio-oil. This will enhance the production, as well as the use of bio-oil as transport fuel substitute or/ and chemicals. The present inventors have found the resulting bio-oil obtained by means of the method to have a reduced content of soot, a reduced viscosity, enhanced storage- life, and a lighter colour, than conventionally obtained bio-oil. Accordingly, as opposed to the prior art pyrolysis oil, which is usually black and opaque, the bio-oil of the invention is typically yellow to brown in colour, and essentially transparent.
Recently, the inventors found that step (c) of the above generic embodiment of the method can be substantially enhanced by providing additional hydrogen radicals (H*) to the process, which radicals can be readily generated, using electrical means 50, from the high-temperature steam present in the process, that is in steps (b) and (c).
The inventors have found that, at the relevant temperature, water molecules (H2O) of the preheated high-temperature steam will to some extent dissociate into radicals (H* and OH*). This is presently believed to the main reason for the observed hydro- genation and oxygenation in the above article by Kantarelis et al. Especially the hydrogen radicals (H*) are believed to effectively contribute to the deoxygenation of oxygenated species in the pyrolysis gas by reacting with said oxygenated species. The type of deoxygenation of the invention can therefore be designated as hydrode- oxygenation (HDO).
According to the invention, the high-temperature steam consequently serves the dual purposes of both constituting a heat carrying agent, which supplies the major part of the necessary heat for effecting pyrolysis, and also constituting a source of hydrogen radicals, thus also supplying a reactive agent (H*) that will serve to deoxy- genate oxygen containing species in the pyrolysis gas, whereby the bio-oil, obtained upon quenching, will be upgraded in this respect and exhibit a low oxygen content.
The provision of additional hydrogen radicals in the process will therefore further improve the quality of the resulting bio-oil, by virtue of additional deoxygenation and hydrogenation.
Accordingly, in a preferred embodiment of the method, additional hydrogen radicals (H*) are being generated and supplied to the method. The additional hydrogen radicals are being formed from the high-temperature steam in using electrical means. Oxygenates formed in pyrolysis step (b) are then brought into contact with the hydrogen radicals thus formed. Thereby, deoxygenation of oxygenates contained in the pyrolysis gas will be enhanced, and the quality of the resulting bio-oil further improved. For large scale operations, the use of a hydrogen radical generator will also serve to offer effective means of controlling the process, in terms of desired extent of hydrogenation and deoxygenation.
In another aspect the present invention relates to a corresponding arrangement for carrying out the above preferred inventive method comprising: a pyrolysis reactor 30 with the capability of withstanding temperatures in the range of 400-700°C, which reactor exhibits an inlet for a carbonaceous, solid raw material 40, and an inlet for high-temperature steam 28 of a temperature within the interval of 400- 700°C; and quenching means 100 for cooling the pyrolysis gas 60 obtained in the pyrolysis reactor 30, wherein the reactor further comprises electrical means 50 for producing hydrogen radicals (H*) from the high-temperature steam within the reactor.
In a preferred embodiment, the arrangement also comprises separation means 70, such as e.g. a cyclone, for removing char and solid residues from the pyrolysis gas
before quenching.
In yet a preferred embodiment the quenching means 100 is also provided with electrical means 50 for producing hydrogen radicals (H*) from the high-temperature steam within the quenching means.
In a preferred embodiment, an arrangement for carrying out the above generic inventive method comprises: a pyrolysis reactor 30 with the capability of withstanding temperatures in the range of 400-700°C, which reactor exhibits an inlet for a car- bonaceous, solid raw material 40, and an inlet for high-temperature steam 28 of a temperature within the interval of 400-700°C; and quenching means 100 for cooling the pyrolysis gas obtained in the pyrolysis reactor 30, wherein the arrangement further comprises separation means 70 for removing char and solid residues 80 from the pyrolysis gas 60 before quenching, so as to obtain clean pyrolysis gas 90, which then can be quenched in cooler 100 so as to form bio-oil 120.
Another objective is the online reforming of complex long chain hydrocarbons and cyclic hydrocarbons, formed from the carbonaceous, solid raw material fed into the process upon pyrolysis thereof, to enhance the hydrogenation of the produced bio- oil.
Other objects and advantages of the present invention will become obvious to the reader skilled in the art and it is intended that these objects and advantages are within the scope of the present invention.
According to the embodiments of the present invention, biomass undergoes pyrolysis producing liquid oil, value added products and gaseous fuel products. The term liquid oil' as used herein means a liquid which is obtained upon quenching of the pyrolysis gases, and which is in a liquid state at room temperature. The terms liq- uid oil, bio-oil and pyrolysis liquid have been used interchangeably herein.
The inventive method is carried out in continuous operation.
BRIEF DESCRIPTION OF THE DRAWINGS
Figure 1 shows a general system flow diagram, wherein reference numeral 28 denotes a high-temperature steam inlet, 30 denotes a pyrolysis reactor, 40 carbona- ceous feeding, 50 hydrogen radical generators, 60 pyrolysis gas generated from pyrolysis reactor, 70 a cyclone separator, 80 char and solid residues, 90 clean pyrolysis gas, 100 a cooler, 1 10 syngas obtained from the process, and 120 denotes bio- oil obtained from the inventive process. Figure 2 shows a pilot batch plant, which was used for carrying out the inventive method in batch mode operation on a pilot scale, wherein 1 -4 denotes gas nozzles, 5 air nozzle, 6 methane nozzle, 7 gas burner, 8 combustion chamber, 9 ceramic honeycomb, 10 cooling chamber, 1 1 lid, 12 online gravimetric measurement, 13 cooling nitrogen nozzle, 14 perforated basket with sample, 15 flue gases, 16 sam- pling line, 17 gas washing bottle for liquid collection, 18 reaction chamber, 19 window, 20 thermocouple for steam temperature measurement, 21 thermocouple for sample temperature measurement, 22 cooling bath of -15°C to - 10°C, 23-26 cooling water, and 27 denotes a gas chromatograph. The pilot batch plant is not an embodiment of the arrangement of the invention.
DETAILED DESCRIPTION OF THE INVENTION AND PREFERRED EMBODIMENTS THEREOF
Introduction of high-temperature steam in biomass pyrolysis process results in a low oxygen content upgraded bio-oil with an O/C ratio less than 0.2. The introduction of high-temperature steam allows the reforming and cracking of heavy bio-oil molecules to lower molecular weight substances while the hydrogen radicals that are present due to steam dissociation reactions are taking part in the hydrodeoxy- genation (HDO) of the primary oxygenated species resulting from the pyrolysis. The inventive system includes a biomass pyrolysis reactor 30 working in the temperature range of 400°C to 700°C, into which reactor high-temperature preheated steam of a temperature within the range of 400°C to 700°C is injected. The stream is not only acting as a heating agent supplying the major part of the heat necessary for the pyrolysis, but also acting as a hydrogen donor, providing reactive hydrogen which will react with oxygenates in the pyrolysis gas, and thereby reduce the oxygen: carbon in order to get rid of oxygen.
The preferred working temperature range of the pyrolysis reactor, and also of the high-temperature steam being fed into the reactor, is within the interval of about 440°C to 600°C.
The heat required for the pyrolysis is mainly provided by the high-temperature steam entering the reactor. However, additionally heating will typically be required in order to maintain the temperature within the pyrolysis reactor within the range of 400-700°C. The additional heat can be provided by electrical heating of the reac- tor, and/ or by means of hot flue gases being passed into the pyrolysis reactor from combustion outside the reactor, such as e.g. from upstream generation of high- temperature steam. Such flue gases could enter the pyrolysis reactor together with the high-temperature steam, or via a separate inlet. Accordingly, the pyrolysis reactor may be provided with means for electrical heating thereof and / or an inlet for hot flue gases.
In a preferred embodiment the pyrolysis reactor uses a fixed or fluidized bed, preferably a fluidized bed, to which the carbonaceous raw material is being fed. The pyrolysis reactor is preferably operating at essentially atmospheric pressure, since otherwise the bio-oil yield will decrease. Also, for the same reason, the high- temperature steam is fed into the pyrolysis reactor preferably at about atmospheric pressure. Preferably, the pyrolysis reactor is provided with electrical means for generating hydrogen radicals from the high-temperature steam in the pyrolysis reactor. Hydrogen radicals can e.g. be generated by means of electrical discharge, such as electrodes, or plasma. The electrical discharge is preferably operating continuously during the pyrolysis. In the case of a fixed or fluidized bed, the electrical means (discharge or plasma) is preferably located in the freeboard of the bed.
In the inventive process, the bio-oil produced during the pyrolysis process is simultaneously cracked and reformed in the presence of steam to produce ¾. Produced hydrogen can take part in hydrogenation reactions; in addition hydrogen radicals from the highly superheated steam, and/or from the electric spark, or plasma, can
also take part in the HDO of the of the oxygenated species contained in the pyroly- sis gas, so as to produce an upgraded bio-oil. The hydrogen radicals are very reactive during thermal cracking.
Hydrogen radicals are hydrogen donors enhancing the online upgrading of the produced bio-oil. The above mentioned can be schematically depicted by the following scheme:
+ H *
CxH Oz > -CH2 - y -H20
The above mentioned features result in a low oxygen content bio-oil, which is essential for the stability and overall quality of the resulting bio-oil as a fuel.
The co-produced gas is a hydrogen rich gas and therefore a valuable gas product.
The solid residue produced from the process exhibits enhanced surface characteristics that can enhance the exploitation of the material.
The pyrolysis vapors leaving the reactor are being passed through a tube and are rapidly quenched. With reference to the pilot plant illustrated in Figure 2, this can be accomplished using gas washing bottles at temperatures of - 10°C down to - 15°C, and a cooling bath. In large scale plants, the cooling temperature will typically be atmospheric or ambient. Condensable molecules are then obtained as a liquid, i.e. as bio-oil.
Having read the instant disclosure, optimum dimensional relationships for the parts of the invention, including variations in size, materials, shape, form, function and manner of operation, assembly and use, will be readily apparent and obvious to one skilled in the art.
Therefore, the foregoing is considered as illustrative only of the principles of the invention. Further, since numerous modifications and changes will readily occur to
those skilled in the art, it is not desired to limit the invention to the exact construction and operation shown and described, and accordingly, all suitable modifications and equivalents may be resorted to, falling within the scope of the invention as defined in the appended claims.
In accordance with the present invention, and with reference to Fig. 1 , there is provided a process for converting carbonaceous materials to liquid. In a preferred embodiment the process comprises the following steps. Feeding preheated high- temperature steam 28 of a temperature within the range of 400°C to 700°C, which can be generated by a regenerative system, an electrical heater, a boiler, or from combustion of hydrogen and oxygen. Feeding the carbonaceous, solid material 40 into pyrolysis reactor 30. The reactor 30 is operating in the temperature of 400°C to 700°C. The temperature of reactor 30 is maintained by an electric heater (not shown), or by hot flue gases from combustion of e.g. biomass, or syngas 110 ob- tained from the process, or solid residue 80 (predominantly char) generated from pyrolysis reactor 30. A hydrogen radical generator 50 is installed in the reactor 30. This generator produces hydrogen radicals (H*), which are used as a hydrogen donor for the deoxygenation process of the pyrolysis gas. The stream of pyrolysis gas 60 generated from the pyrolysis reactor 30 passes through a cyclone separator 70. Here, solid residues 80 can be separated from the pyrolysis gas stream 60. A clean pyrolysis gas stream 90 exiting cyclone 70 flows into a cooler 100. Here, most of the gas is cooled to produce a pyrolysis liquid (i.e. bio-oil) 120. The pyrolysis liquid can then can be collected from the process. A hydrogen radical generator 50 is also installed in the cooler 100 in order to provide hydrogen radicals also at this loca- tion, enabling additional deoxygenation reaction of the gaseous oxygenates and hy- drogenation reaction of gaseous unsaturated compounds before being converted into a liquid state.
The following Example is provided for a better understanding of the features, as- pects, and advantages of the present invention.
EXAMPLE
The principal steps of the inventive process were carried out in batch-wise operation mode on a pilot scale apparatus as shown in Fig. 2. The pilot scale apparatus is based on a universal batch reactor, which reactor has been developed for a different
purpose and has been described in more detail by Anna Ponzio, Sylvester Kalizs, Juliette Promelle, Wlodzimierz Blasiak, Susumo Mochida, Combustion of wood pellets in a high temperature and oxygen diluted environment, Proceedings from 6th Hi- TACG conference 2005 , Essen 2005. The pilot scale plant shown in Figure 2 is not an arrangement according to the invention.
The experimental pilot scale rig shown in Figure 2 consists of a horizontal combustion chamber with an inner diameter about 0. 1 m. High-temperature steam was obtained as follows. Methane and air were fed via nozzles 5 and 6 to the gas burner 7. As the fuel burns in the combustion chamber 8 the hot flue gases will heat the ceramic honeycomb 9 and flow through the second part of the reactor 18 and towards the reactor's outlet 15. The rig is run in heating mode until the desired temperature of the honeycomb is reached. Once the proper temperature is reached, the methane feed is shut off and the experimental stage started. The proper feed gas (in this case N2) is set by adjusting the flow of steam and the resulting heating agent is fed through feed gas nozzles 1-4 and is heated by the hot honeycomb 9. The heated agent temperature is measured by a thermocouple 20. A portion of a feedstock is attached to a piston as a thin bed in a basket 14 fabricated by metal net for this purpose. The lid 11 with the piston and the feedstock sample is attached to the rig, with the feedstock sample in a small cooling chamber 10 where it is cooled by nitrogen 13. The experiment starts when the sample on the piston is pushed down into the reactor chamber 18 from above. Once the sample is in the chamber, the sample is visible through glass window 19. The temperature of the sample is measured by a thermocouple 21. Thereafter, the basket is lifted from the chamber to the cooling chamber 10 in order to quench the reactions through cooling with nitrogen. The pyrolysis vapors leaving the reactor are passed a sampling line 16 and they are rapidly quenched by gas washing bottles 17 to temperatures of - 10°C down to - 15°C, using a cooling bath 22. Condensable molecules are obtained as a liquid. The gases are driven to GC analyzer 27.
Bamboo has been tested in above facility. The particle size of the bamboo was about 200-500 μπι. The elemental analysis was performed using a Vario Micro Elemental Analysis instrument. The alkali content and other metals that can be found in the ash of the material were analyzed using a PE5300DV inductively coupled plasma spectrometer.
Table 1 Analysis of the raw material
Moisture [%wt] 1.87
Cellulose [%wt] 39.61
Hemicellulose [%wt] 17.53
Lignin [%wt] 22.61
Extraction mat- ter[%wt] 18.38
Ultimate Analysis
C [% wt] 47.98
H [% wt] 6.59
O [% wt] 42.875
N [% wt] 1.93
Al [% wt] 0.004
Ca [% wt] 0.044
Fe [% wt] 0.05
K [% wt] 0.417
Mg [% wt] 0.044
Mn [% wt] 0.01
Na [% wt] 0.042
P [% wt] 0.012
Zn [% wt] 0.002
The quality of the inventive bio-oil generated from bamboo via fast pyrolysis in presence of steam was assessed. The results show that the ratio H/C is 1.51 , and the ratio of O/C is 0. 16. Both values demonstrate a good quality of the resulting bio-oil.
The water content in the resulting liquids were around 30% and the liquids obtained were fully miscible in water.
The bio-oils obtained were transparent, brown liquids.
Elemental composition of bio-oil obtained from steam pyrolysis at 797 K (523.85°C)
Component Content [%wt]
High-Temperature
Steam Pyrolysis at
797 K (523.85°C) (this
study)
C 74.44
H 9.55
O 16.01
During the pyrolysis process of bamboo, the yields of different productions at different temperature are given below.
Temp. K Char Bio-oil Gases
(°C) (solid) wt% wt% wt%
797 25 55 20
(523.85)
865 21 43 36
(591.85)
Claims
1. A method of producing bio-oil from a carbonaceous, solid raw material (40) selected from waste materials and biomass, and mixtures thereof, comprising the steps of:
(a) providing a carbonaceous, solid raw material (40);
(b) subjecting the carbonaceous, solid raw material to conditions effective for accomplishing fast pyrolysis of said carbonaceous, solid raw material;
(c) subjecting the oxygenates formed in step (b) to conditions effective for ac- complishing deoxygenation of said oxygenates; and
(d) cooling the gaseous components formed in step (c), in order to obtain liquid bio-oil,
wherein steps (b) and (c) are accomplished by means of subjecting the carbonaceous, solid raw material to high-temperature steam at a temperature within the interval of 400-700°C.
2. The method of claim 1 , wherein steps (b) and (c) are being carried out in the same reactor (30).
3. The method of claims 1 or 2, wherein there is no intervening condensation or recovery of pyrolysis liquid between steps (b) and (c).
4. The method of any one of claims 1 -3, wherein the cooling step (d) is multi- staged.
5. The method of any one of claims 1 -4, wherein step (c) is enhanced by the following additional steps:
(cl) generation of hydrogen radicals (H*) from the high-temperature steam being used in steps (b) and (c) by active, electrical means (50); and
(c2) contacting the oxygenates formed in step (b) with hydrogen radicals (H*) formed in step (cl).
6. The method of any one of claims 1 -5, wherein an additional step (e) is included between steps (c) and (d), wherein solid material (80) is separated from the gaseous components (60) obtained from steps (b) and (c), before cooling of the gaseous components (90) in step (d) to form bio-oil ( 120).
7. An arrangement for carrying out the method of claim 1 comprising:
a pyrolysis reactor (30) with the capability of withstanding temperatures in the range of 400-700°C, said reactor being provided with an inlet for a carbonaceous, solid raw material (40), and an inlet for high-temperature steam (28) of a temperature within the interval of 400-700°C; and
quenching means (100) for cooling the pyrolysis gas obtained in the pyrolysis reactor (30),
wherein the reactor (30) further comprises electrical means (50) for producing hydrogen radicals (H*) from the high-temperature steam in the reactor.
8. The arrangement of claim 7, further comprising means (70) for separating solids from the pyrolysis gas (60) obtained from the pyrolysis reactor (30) before cooling thereof to form bio-oil (120).
9. An arrangement for carrying out the method of claim 1 comprising:
a pyrolysis reactor (30) with the capability of withstanding temperatures in the range of 400-700°C, said reactor being provided with an inlet for a carbonaceous, solid raw material (40), and an inlet for high-temperature steam (28) of a temperature within the interval of 400-700°C; and
quenching means ( 100) for cooling the pyrolysis gas (60) obtained in the pyrolysis reactor (30),
wherein the arrangement further comprises means (70) for separating solids (80) from the pyrolysis gas (60) obtained from the pyrolysis reactor (30) before cooling thereof into bio-oil.
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CN116286067B (en) * | 2023-02-01 | 2024-03-15 | 四川大学 | Long-period stable operation method and device for producing gasoline and diesel oil by biomass |
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CN116286067B (en) * | 2023-02-01 | 2024-03-15 | 四川大学 | Long-period stable operation method and device for producing gasoline and diesel oil by biomass |
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