NZ626549B2 - Biomethane production method - Google Patents
Biomethane production method Download PDFInfo
- Publication number
- NZ626549B2 NZ626549B2 NZ626549A NZ62654912A NZ626549B2 NZ 626549 B2 NZ626549 B2 NZ 626549B2 NZ 626549 A NZ626549 A NZ 626549A NZ 62654912 A NZ62654912 A NZ 62654912A NZ 626549 B2 NZ626549 B2 NZ 626549B2
- Authority
- NZ
- New Zealand
- Prior art keywords
- synthesis gas
- gasification
- reactor
- methanation
- specifications
- Prior art date
Links
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 22
- 238000002309 gasification Methods 0.000 claims abstract description 56
- UGFAIRIUMAVXCW-UHFFFAOYSA-N carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 44
- 229910002091 carbon monoxide Inorganic materials 0.000 claims abstract description 43
- 230000015572 biosynthetic process Effects 0.000 claims abstract description 38
- 238000003786 synthesis reaction Methods 0.000 claims abstract description 38
- 230000002194 synthesizing Effects 0.000 claims abstract description 38
- 239000002028 Biomass Substances 0.000 claims abstract description 34
- 238000000746 purification Methods 0.000 claims abstract description 25
- 239000000203 mixture Substances 0.000 claims abstract description 15
- 239000004215 Carbon black (E152) Substances 0.000 claims abstract description 13
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 13
- 239000007789 gas Substances 0.000 claims description 49
- 229910052739 hydrogen Inorganic materials 0.000 claims description 17
- 239000001257 hydrogen Substances 0.000 claims description 16
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 12
- UFHFLCQGNIYNRP-UHFFFAOYSA-N hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims description 11
- 238000006297 dehydration reaction Methods 0.000 claims description 10
- 238000006243 chemical reaction Methods 0.000 description 28
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 28
- 229910001868 water Inorganic materials 0.000 description 12
- CURLTUGMZLYLDI-UHFFFAOYSA-N carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 7
- 239000001569 carbon dioxide Substances 0.000 description 7
- 229910002092 carbon dioxide Inorganic materials 0.000 description 7
- 239000003054 catalyst Substances 0.000 description 7
- 230000003197 catalytic Effects 0.000 description 6
- 238000000926 separation method Methods 0.000 description 6
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 5
- 235000015450 Tilia cordata Nutrition 0.000 description 5
- 235000011941 Tilia x europaea Nutrition 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 5
- 150000001875 compounds Chemical class 0.000 description 5
- 238000001816 cooling Methods 0.000 description 5
- 150000002431 hydrogen Chemical class 0.000 description 5
- 239000004571 lime Substances 0.000 description 5
- 239000011269 tar Substances 0.000 description 5
- VTYYLEPIZMXCLO-UHFFFAOYSA-L calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 4
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium monoxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 4
- 239000000571 coke Substances 0.000 description 4
- 239000003344 environmental pollutant Substances 0.000 description 4
- 238000005243 fluidization Methods 0.000 description 4
- 238000002347 injection Methods 0.000 description 4
- 239000007924 injection Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- 238000004064 recycling Methods 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- XLOMVQKBTHCTTD-UHFFFAOYSA-N zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 4
- JJWKPURADFRFRB-UHFFFAOYSA-N Carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 238000009833 condensation Methods 0.000 description 3
- 230000005494 condensation Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 239000003345 natural gas Substances 0.000 description 3
- 238000004088 simulation Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 229960003563 Calcium Carbonate Drugs 0.000 description 2
- 229910000019 calcium carbonate Inorganic materials 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000007906 compression Methods 0.000 description 2
- 239000000470 constituent Substances 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 239000010450 olivine Substances 0.000 description 2
- 229910052609 olivine Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- MYMOFIZGZYHOMD-UHFFFAOYSA-N oxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000000197 pyrolysis Methods 0.000 description 2
- 238000002407 reforming Methods 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- 239000011787 zinc oxide Substances 0.000 description 2
- 241001474374 Blennius Species 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 210000003608 Feces Anatomy 0.000 description 1
- ZIBGPFATKBEMQZ-UHFFFAOYSA-N Triethylene glycol Chemical compound OCCOCCOCCO ZIBGPFATKBEMQZ-UHFFFAOYSA-N 0.000 description 1
- 240000008529 Triticum aestivum Species 0.000 description 1
- 238000007792 addition Methods 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000010828 animal waste Substances 0.000 description 1
- ZOXJGFHDIHLPTG-UHFFFAOYSA-N boron Chemical compound [B] ZOXJGFHDIHLPTG-UHFFFAOYSA-N 0.000 description 1
- 229910052796 boron Inorganic materials 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 235000013339 cereals Nutrition 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000004939 coking Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000005336 cracking Methods 0.000 description 1
- 230000004059 degradation Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 150000002484 inorganic compounds Chemical class 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 238000010327 methods by industry Methods 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000001737 promoting Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 239000011299 tars and pitches Substances 0.000 description 1
- 235000021307 wheat Nutrition 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
- -1 zinc oxide ZnO) Chemical class 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B3/00—Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
- C01B3/50—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification
- C01B3/56—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification by contacting with solids; Regeneration of used solids
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B3/00—Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
- C01B3/50—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification
- C01B3/56—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification by contacting with solids; Regeneration of used solids
- C01B3/58—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification by contacting with solids; Regeneration of used solids including a catalytic reaction
- C01B3/586—Separation of hydrogen or hydrogen containing gases from gaseous mixtures, e.g. purification by contacting with solids; Regeneration of used solids including a catalytic reaction the reaction being a methanation reaction
-
- 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
- C10G2300/4081—Recycling aspects
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0913—Carbonaceous raw material
- C10J2300/0916—Biomass
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/164—Integration of gasification processes with another plant or parts within the plant with conversion of synthesis gas
- C10J2300/1656—Conversion of synthesis gas to chemicals
- C10J2300/1662—Conversion of synthesis gas to chemicals to methane (SNG)
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/18—Details of the gasification process, e.g. loops, autothermal operation
- C10J2300/1807—Recycle loops, e.g. gas, solids, heating medium, water
- C10J2300/1823—Recycle loops, e.g. gas, solids, heating medium, water for synthesis gas
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/463—Gasification of granular or pulverulent flues in suspension in stationary fluidised beds
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/48—Apparatus; Plants
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/04—Purifying combustible gases containing carbon monoxide by cooling to condense non-gaseous materials
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K3/00—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide
- C10K3/02—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment
- C10K3/04—Modifying the chemical composition of combustible gases containing carbon monoxide to produce an improved fuel, e.g. one of different calorific value, which may be free from carbon monoxide by catalytic treatment reducing the carbon monoxide content, e.g. water-gas shift [WGS]
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/04—Gasification
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/06—Heat exchange, direct or indirect
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/08—Drying or removing water
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/10—Recycling of a stream within the process or apparatus to reuse elsewhere therein
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/14—Injection, e.g. in a reactor or a fuel stream during fuel production
- C10L2290/145—Injection, e.g. in a reactor or a fuel stream during fuel production of air
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/14—Injection, e.g. in a reactor or a fuel stream during fuel production
- C10L2290/148—Injection, e.g. in a reactor or a fuel stream during fuel production of steam
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/46—Compressors or pumps
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/54—Specific separation steps for separating fractions, components or impurities during preparation or upgrading of a fuel
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L3/00—Gaseous fuels; Natural gas; Synthetic natural gas obtained by processes not covered by subclass C10G, C10K; Liquefied petroleum gas
- C10L3/06—Natural gas; Synthetic natural gas obtained by processes not covered by C10G, C10K3/02 or C10K3/04
- C10L3/08—Production of synthetic natural gas
-
- 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
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
Abstract
Disclosed is a method for the production of biomethane from hydrocarbon feedstock (200), comprising at least the following steps: gasification (201) of the feedstock in order to produce a synthesis gas in a gasification reactor; purification (204), in a purification unit, of the synthesis gas produced during the biomass gasification step; methanisation (206) of the purified synthesis gas in a methanisation reactor; and adjustment to specifications (207) of the gas mixture obtained during the synthesis gas methanisation step, in order to obtain biomethane. During the specifications adjustment step, a flow comprising at least the excess carbon monoxide is recirculated (208) in the gasification reactor. The invention also relates to a device for carrying out the method of the invention. ed during the biomass gasification step; methanisation (206) of the purified synthesis gas in a methanisation reactor; and adjustment to specifications (207) of the gas mixture obtained during the synthesis gas methanisation step, in order to obtain biomethane. During the specifications adjustment step, a flow comprising at least the excess carbon monoxide is recirculated (208) in the gasification reactor. The invention also relates to a device for carrying out the method of the invention.
Description
BIOMETHANE PRODUCTION METHOD
The present invention relates to the field of biomethane production and more
specifically to a method for producing biomethane by gasification of hydrocarbon
feedstock.
Currently, Biomethane (or SNG: Substitute Natural Gas) production can be
achieved by thermochemical biomass conversion.
The biomass may consist of wood residue (chips, sawdust, bark), plant
residue (peel, seeds, stems, cereals, wheat, etc.), farming sector residues, agrifood
waste (fats, slaughterhouse residues), animal waste (manure), waste related to
human activity (slurry), marine seaweed, etc.
This conversion is realized by a method consisting of three main steps:
- gasification of the biomass to produce synthesis gas (syngas)
composed mostly of hydrogen (H ), carbon monoxide (CO), carbon dioxide (CO )
and methane (CH ),
- catalytic methanation that consists of converting the hydrogen and
carbon monoxide into methane and,
- adjusting to specifications, which is aimed at eliminating residual
hydrogen, residual carbon monoxide, water and carbon dioxide so as to produce
biomethane that meets the specifications for injection into the natural gas network,
especially in terms of heating value (HHV) and Wobbe Index.
Biomass gasification is carried out within a reactor in which biomass
undergoes different reaction steps.
The biomass is first subjected to thermal degradation by drying and then to
devolatilization of organic matter to produce a carbonaceous residue (char), a
synthesis gas (H , CO, CO , CH , etc.), and condensable compounds contained
2 2 4
within the syngas (tars and more generally, whatever is condensable). The
carbonaceous residue can then be oxidized by the gasification agent (water vapor,
air, oxygen) to produce hydrogen, carbon monoxide, etc. Depending on its nature,
this gasification agent can also react with the tars or the major constituent gases.
Thus, if it is water vapor (H O), a gas reaction to water (or WGS: Water Gas Shift)
occurs in the gasification reactor according to the following equilibrium:
CO + H O ⇔ H + CO
2 2 2
The reactor pressure has little effect on this reaction. In contrast, the
equilibrium is strongly linked to the reactor temperature and to the initial
concentrations of reagents.
For existing methods, the H /CO ratio never exceeds two at the end of the
gasification step and, for example, it is of the order of 1.8 for the dual fluidized bed
FICFB (Fast Internally Circulating Fluidized Bed) concept. This H /CO ratio is an
important factor for biomethane production as the methanation reaction that makes
the production of methane possible and on which the biomethane production method
is based is as follows:
CO + 3 H ⇔ CH +H O
2 4 2
To maximize methane CH production and minimize excess carbon
monoxide, hydrogen and carbon monoxide should be in a 3:1 stoichiometric ratio.
However, even by respecting to this ratio, the reaction remains incomplete because
of the chemical equilibrium. The 3:1 ratio maximizing the reaction is achieved by
performing an additional WGS reaction. This can be done prior to methanation in a
dedicated reactor, in the presence of specific catalysts. It is possible for it to be
performed directly in the same reactor as the methanation, with a possible
adjustment of the catalyst. In both cases, this reaction requires a significant injection
of water vapor.
On output from the gasifier, the mass fraction of water in the synthesis gas is
generally of the order of 30%. It comes partly from the biomass moisture and, in the
case of certain methods, partly from direct injection of vapor into the gasifier.
However, the step of syngas purification to remove pollutants before methanation (in
particular, removing tars, dust, inorganic compounds, etc.) requires a cooling
operation in which the water present therein is largely condensed and eliminated,
and is thus no longer available for an additional WGS step.
Indeed, after these purification steps, the mass fraction of water is reduced
to about 5%, which concentration is insufficient to achieve the additional WGS
reaction and achieve optimum operation of the chain of methods in its typical
configuration. Thus, to make it possible to adjust the H O/CO ratio required for the
methanation reaction, injection of water vapor becomes essential to avoid excess
carbon monoxide before the step of adjusting to specifications. This water vapor is
generally produced by recovering high temperature energy from the method; such
energy would be easily marketable and constitutes a loss of direct profitability of the
system. In addition, implementing the WGS translates into increased complexity of
the method and an increase in capital expenditure and operating costs.
Some known methods from the family of fast internally circulating fluidized bed
reactor (FICFB) gasification systems offer some solutions to these problems. In these
methods, biomass gasification is implemented in a first reactor by contact with a hot
heat transfer medium. This medium and a portion of the pyrolysis char formed in this
reactor are extracted continuously at the base of the bed. They are then sent to a
second reactor (combustor) where a fluidization medium is heated by the combustion
of the char and a fuel booster before being reinjected into the gasifier. The heat
transfer medium can consist of an inert solid (e.g. sand) or a mineral (olivine) with
catalytic properties for cracking or reforming tars coming from the imperfect
conversion of biomass. In this case, the H /CO ratio achieved is between 1.3 and 1.8.
International application WO 01/23302 describes a method belonging to this
family of FICFB methods, the AER (Absorption Enhanced Reforming) method, which
relates to syngas production that can be used directly in SNG-production
methanation reactors. The method described in this application makes it possible to
achieve the optimum specifications (H O/CO ratio greater than or equal to three)
required for the methanation step.
In this AER method, the fluidization medium is no longer olivine but lime
(CaO). In the gasifier, the lime absorbs the present carbon dioxide to form calcium
carbonate CaCO , according to the reaction below for a temperature range of 650 to
750°C.
CaO (s) + CO (g) → CaCO (s)
Because of the capture of the carbon dioxide, the WGS reaction, which is
balanced, is switched to hydrogen production and carbon monoxide reduction, which
leads to an increase in the H /CO ratio. Calcium carbonate is then converted into
lime by the inverse reaction at a higher temperature in the combustor. H O/CO ratios
of five to seven can be achieved in this way. Higher ratios, while making it possible to
minimize the risk of coking on the methanation catalyst, can result in a decrease in
the overall biomethane production yield and difficulties in separating the hydrogen
and the syngas for adjusting the natural gas to specifications. The use of lime also
leads to a slight decrease in the concentration of methane in the syngas. In addition,
while lime is a good fluidization medium, its mechanical fragility makes it very prone
to attrition phenomena and limits its lifespan.
A catalytic method, typically in fixed bed reactors, is also known from patent
application US2010/0286292, which proposes to incorporate a WGS reactor into the
conversion chain in order to adjust the H O/CO ratio close to the methanation's
stoichiometry. A disadvantage of this method is that it is necessary to inject a
significant quantity of water vapor, firstly to perform the additional WGS reaction and
secondly, to limit the deposits of coke on the catalysts.
Another method described in documents EP1568674 and WO2009/007061
relates to the production of SNG from biomass gasification. This method consists of a
purification of compounds such as hydrogen sulfide (H S) or Carbonyl sulfide (COS)
by physical or chemical adsorption in fixed beds of activated carbon (AC), of metal
oxides (e.g. zinc oxide ZnO), and methanation in a fluidized bed of catalytic particles
with a particle size of 20 to 2,000 µm. Additional fluidization water vapor can be
supplied to the reactor and recycling of hydrogen coming from the adjustment to
specifications may occur. This method also has the disadvantage of requiring
additional methanation and/or separation steps that increase the complexity of the
method.
The purpose of the present invention is therefore to overcome one or more
of the disadvantages of the prior art by proposing a method aiming to increase the
conversion of biomass into biomethane and improve the overall energy efficiency
thereof. The method does not require modifying the design of the gasification and/or
methanation reactors and requires no additional steps, in particular the WGS step,
before or in parallel with methanation.
To achieve this, the present invention proposes, according to a first aspect, a
method for producing biomethane from hydrocarbon feedstock, comprising at least
the following steps:
- gasification of the feedstock in order to produce a synthesis gas in a
gasification reactor;
- purification, in a purification unit, of the synthesis gas produced
during the hydrocarbon feedstock gasification step;
- methanation of the purified synthesis gas in a methanation reactor;
- adjustment to specifications of a gas mixture obtained during the
synthesis gas methanation step, in order to obtain biomethane;
during the step of adjustment to specifications, a flow comprising at least the
excess carbon monoxide being recycled towards the gasification reactor.
This recycling leads to an increase in the amount of carbon monoxide in the
gasifier, thus promoting the production of hydrogen according to the thermochemical
equilibria described by the WGS reaction directly within this same reactor. The
increase in this amount of hydrogen itself leads to increased methane production
during the methanation step.
According to an embodiment of the invention, the hydrocarbon feedstock is
biomass.
According to an embodiment of the invention, the recycled flow comprises
residual hydrogen.
According to an embodiment of the invention, the recycled flow comprises
residual methane.
According to an embodiment of the invention, on exit from the gasification
reactor, the temperature of the synthesis gas is between 600 and 1000° C.
According an embodiment of the invention, the method comprises a heat
exchange step after the gasification step to cool the synthesis gas to the ambient
temperature.
According an embodiment of the invention, the heat exchange step is carried
out before the purification step.
According to an embodiment of the invention, the method comprises a
dehydration step carried out after the heat exchange step.
According to an embodiment of the invention, the method is performed at a
pressure of 0.5 to 70 bar.
According to an embodiment of the invention, the temperature of the gas
mixture obtained on output from the reactor is between 250 and 700°C.
According an embodiment of the invention, the flow obtained after the step of
adjustment to specifications is at ambient temperature.
This invention envisages, according to a second aspect, a device for
producing biomethane from hydrocarbon feedstock comprising at least:
- a gasification reactor carrying out a gasification of the feedstock to
produce a synthesis gas in a gasification reactor;
- a purification unit performing a purification of the synthesis gas
produced by the feedstock gasification reactor;
- a methanation reactor realizing a methanation of the purified
synthesis gas;
- a means of adjustment to specifications of the gas mixture obtained
during the synthesis gas methanation step, in order to obtain biomethane,
the means of adjustment to specifications being designed to recycle a flow
comprising at least excess carbon monoxide in the gasification reactor.
Other goals, features and advantages of the invention will be better
understood in reading the following description, with reference to the drawings in an
appendix given as an example:
- figure 1 is a schematic representation of an embodiment of a device of the
prior art;
- figure 2 is a schematic representation of the implementation of a particular
embodiment of the method according to the invention;
- figure 3 is a schematic representation of a particular embodiment of the
device that is the subject of the invention; and
- figure 4 is a schematic representation of the implementation of a particular
embodiment of the method according to the invention.
Although described using the example of biomass, the method according to
the invention can be applied to all products likely to be gasified: biomass, coal, coke,
waste, etc., and more generally to all hydrocarbon feedstocks.
The particular embodiment of the method envisaged by the present invention
illustrated in figure 2 and implemented in the device illustrated in figure 3 requires at
least the following steps, which are identical to those described in the prior state of
the art:
- gasification (201): conversion of the hydrocarbon feedstock and, for
example, the biomass into synthesis gas (syngas);
- purification (204) of the synthesis gas produced during the hydrocarbon
feedstock gasification step to remove polluting components harmful to the lifespan of
the catalyst;
- methanation (206) by catalytic conversion of the syngas into
biomethane;
- adjustment to specifications (207) of the gas mixture obtained in the
step of methanation of the synthesis gas to separate the biomethane from the other
constituents, in particular hydrogen, residual carbon monoxide, water and carbon
dioxide, and thus adjust the composition of the biomethane to specifications.
The biomass, being at ambient temperature and more specifically at a
temperature equal to 20°C, circulating in a biomass supply line (100), supplies a
gasification reactor (10). The biomass undergoes a thermochemical conversion in
this gasification reactor (10), to form during the drying/pyrolysis and gasification step
a syngas containing hydrogen, carbon monoxide, carbon dioxide, water, tars and
pitches and/or compounds with the general formula C H , etc. This syngas flows in
the syngas circulation line (1).
Before exiting the reactor, the composition of this gas changes under the
action of the water vapor (injected at a temperature of between 160 and 500°C and
preferably equal to 400°C) or oxidizing agent (oxygen, air, etc.) This change in
composition occurs, firstly, with the thermochemical equilibria in homogeneous phase
and, secondly, because of the production of compounds by heterogeneous phase
gasification of part of the char.
On exit from the gasifier (10) the syngas is at a temperature of between 600
and 1000°C, preferably between 800 and 900°C and very preferably equal to 850°C.
The resulting syngas, thus purified of these pollutants (tars, COS, H S, etc.) before
supplying a methanation reactor (20) then supplying, via a supply line (4), a unit (30)
making the step of adjustment to specifications (also called separation of
compounds) possible. At the end of these steps, the method makes it possible to
obtain biomethane (31).
Under these conditions, the H /CO ratio before methanation is lower than the
stoichiometric ratio and the methanation reaction can only be at its highest for the
missing species, in this case hydrogen. On exit from the methanation reactor (20) the
temperature of the biomethane is between 250 and 700°C, and preferably equal to
300°C. In addition to the biomethane produced, the gas output from the methanation
reactor therefore contains excess carbon monoxide which has not reacted.
The gas mixture produced during the methanation step is split into four
flows:
− a first flow comprising methane which constitutes the biomethane itself,
intended to be used;
− a second flow comprising carbon dioxide;
− a third flow comprising water vapor; and
− a fourth flow comprising at least excess carbon monoxide, and possibly
hydrogen which has not reacted because of the thermochemical equilibria.
In particular embodiments of the method according to the invention, this
fourth flow comprising at least excess carbon monoxide is recycled (208) within the
gasification reactor.
After the adjustment to specifications step, the various flows are at ambient
temperature and preferably at a temperature equal to 20°C.
Since it is thus not necessary to utilize the WGS reaction upstream of or in
parallel with the methanation reaction to effect an adjustment of the H /CO ratio, an
energy and matter gain is achieved equivalent to the flow of this vapor which is
ordinarily added.
According to embodiments of the invention, to remedy any deposit of coke
on the surface of the catalyst, due to the operation of the methanation reactor in
these sub-stoichiometric conditions and for limited H O concentrations, a specific
treatment of the catalyst is used, such as for example doping with boron or with a
suitable catalytic support, in particular by adjusting its acidity.
According to embodiments of the invention, in order to limit the coke deposit,
a limited intake of water vapor is performed to adjust its concentration before
methanation, either directly or by adjusting the temperature of the upstream wash.
In relation to the step of adjusting the biomethane to specifications, which is
typically a separation step, the following methods, for example, are used: PSA
(Pressure Swing Adsorption); TSA (Temperature Swing Adsorption); membrane
separation; amine chemical absorption or physical absorption with triethylene glycol.
These various technologies can be used singly or in combination with each other.
According to embodiments illustrated in figure 4, the gasification step (201)
is followed by a heat exchange step (202) to cool the syngas before passing into the
purifier (16). In this way, the flow of syngas, which is at a temperature of between
600 and 1000°C, preferably between 800 and 900°C and very preferably equal to
850°C after passing through a heat exchanger (14) is at a temperature between 4
and 80°C, preferably between 25 and 35°C, and very preferably at ambient
temperature (more precisely, equal to 20°C).
At the end of this heat exchange step (202), the water is partially removed
from the syngas (circulating in the duct (2) positioned between the heat exchanger
(14) and the dehydration unit (15)), which is cooled and dried (203) in a dehydration
unit (15) from which the condensates are removed. This step of dehydration by
cooling and condensation of the water vapor (203) is followed by a step of purification
(204) in a purification unit (16) in which the flow is brought by the duct (3) positioned
between the dehydration unit (15) and the purification unit (16).
The method according to the invention can be applied generally to all
gasifiers.
Preferably, the method can be applied to methods producing a gas without
dilution by the nitrogen of the air.
The method is not specific to any particular methanation process and can be
applied to all these methods. In the case of fixed bed recycling type of methods, the
method even makes a decrease in the rate of recycling possible.
The method according to the invention is, in embodiments, utilized at a
pressure of between 0.5 and 70 bar, and preferably between 1 and 5 bar.
The present invention also envisages a device for producing biomethane
from hydrocarbon feedstock, comprising at least:
- a gasification reactor (10) carrying out a gasification of the feedstock
to produce a synthesis gas in a gasification reactor;
- a purification unit (16) performing a purification of the synthesis gas
produced by the feedstock gasification reactor (10);
- a methanation reactor (20) realizing a methanation of the purified
synthesis gas;
- a means of adjustment to specifications (30) of the gas mixture
obtained during the synthesis gas methanation step, in order to obtain biomethane.
The adjustment to specifications means (30) of this device is designed to
recycle a flow comprising at least excess carbon monoxide towards the gasification
reactor.
The invention will now be illustrated with the following non-limiting examples.
Examples:
In order to demonstrate the value of the invention, comparative simulations
of the previous solutions and of the present invention were performed with a CAPE
(Computer Aided Process Engineering) process simulation tool.
The simulations were conducted for one metric ton of dry biomass to be
converted per hour to obtain biomethane.
In the following examples, the flows correspond to:
- flow 100, the biomass;
- flow 101, the vapor injected into the gasifier;
- flow 1, the syngas output from gasifier;
- flow 2, the cooled syngas;
- flow 3, the dehydrated syngas;
- flow 102, the condensates,
- flow 103, the vapor for the additional WGS;
- flow 4, the biomethane before adjustment to specifications,
- flow 104, the CO/H ;
- flow 105, the CO ;
- flow 106, the H O;
Comparative example according to the prior art:
In this example according to the prior art (illustrated in figure 1), the biomass
is introduced into a gasification reactor (10), in which it undergoes a thermochemical
conversion; then the synthesis gas (or syngas) output from the gasifier after passing
through a heat exchanger (14) passes into a dehydration unit (15). This step of
dehydration by cooling and condensation of the water vapor is followed by a step of
purification (204) in a purification unit (16) and a WGS step in a WGS reactor (17)
with the addition of water vapor. The syngas then undergoes a compression step
(205) in a compressor (18). The syngas thus produced and purified of these
pollutants supplies a methanation reactor (20) then undergoes a separation step in a
dedicated unit for adjustment to specifications (30).
Table 1 summarizes the conditions and results of the simulation for the
method according to the prior art at different steps in the method and for the various
effluents.
Table 1
Examples according to particular embodiments of the invention:
In this example according to the invention (illustrated in figure 3), the
biomass circulating in a biomass supply line (100) supplies a gasification reactor
(10), in which it undergoes a thermochemical conversion; then the synthesis gas (or
syngas) output from the gasifier after passing through a heat exchanger (14) passes
into a dehydration unit (15). This step of dehydration by cooling and condensation of
the water vapor (203) is followed by a step of purification in a purification unit (16).
The syngas then undergoes a compression step (205) in a compressor (18). The
syngas thus produced and purified of these pollutants supplies a methanation reactor
(20) then undergoes a separation step in a unit for adjustment to specifications (30).
Table 2 summarizes the conditions and results of the simulation for
embodiments of the method according to the invention at different steps of the
method and for the various effluents.
Table 2
Analysis of the results
The energy yield of the method based on methane production is defined by
the following relation:
m PCI
CH * CH
m PCI
biomass * biomass
wherein:
m represents the mass of methane.
m represents the mass of biomass.
biomass
PCI represents the lower heating value of the methane.
PCI represents the lower heating value of the biomass.
biomass
The simulations carried out show that this yield is increased to 61.2% by
utilizing the proposed solution in embodiments of the present invention, while the
existing solutions only make it possible to achieve 54.2%, i.e. a 7 % increase.
In embodiments, the method according to the invention is based on
recirculation of the CO/H flow to the gasifier. The recirculation flow rate associated
therewith is intimately linked to the partial pressure of water in the gasifier (water
introduced with the biomass and possibly as gasification agent). The consequence of
too low a concentration in the gasifier is a very high recirculation flow rate without any
consequent impact on the quantity of CH produced.
Embodiments of the method that is the subject of the present invention thus
make it possible, in comparison with the methods of the prior art, to achieve:
- an increased hydrogen flow produced by the gasification, from
23.75kmol/h to 27.27 kmol/h;
- a shift vapor flow (40,00 kmol/h) removed;
- a decrease in the water flow to be removed on output from methanation
from 50.57 kmol/h to 11.85 kmol/h, resulting in a saving in the cooling energy
consumed by the method;
- an adjustment to specifications of the volume fraction of hydrogen, a
complex operation and source of loss of efficiency of the method, which is no longer
needed because of a H /CH ratio on output from the methanation reactor output that
goes from 6.3% to 2.7%. This improvement is mainly due to the excess of carbon
monoxide in the methanation reactor.
- a flow of biomethane (SNG) on output from the system that goes from
11.81 kmol/h to 13.33 kmol/h, a 12.9% gain.
The scope of this invention is not limited to the details given above and
allows embodiments in many other specific forms without moving away from the
invention's field of application. Therefore, the present embodiments should be
considered illustrative, and can be modified without however moving outside the
scope defined by the claims.
Claims (12)
1. Method for the production of biomethane from hydrocarbon feedstock, comprising at least the following steps: 5 - gasification (201) of the feedstock in order to produce a synthesis gas in a gasification reactor (10); - purification (204), in a purification unit (16), of the synthesis gas produced during the biomass gasification step; - methanation (206) of the purified synthesis gas in a methanation 10 reactor (20); - adjustment to gas specifications (207) of the gas mixture obtained during the synthesis gas methanation step, in order to obtain biomethane; characterized in that, during the step of adjustment to specifications (207), a 15 flow comprising at least the excess carbon monoxide is recycled (208) towards the gasification reactor (10).
2. Method according to claim 1, characterized in that the hydrocarbon feedstock is biomass.
3. Method according to one of claims 1 or 2, characterized in that the 20 recycled flow comprises residual hydrogen.
4. Method according to one of claims 1 to 3, characterized in that the recycled flow comprises residual methane.
5. Method according to one of claims 1 to 4, characterized in that on exit from the gasification reactor (10), the temperature of the synthesis gas is 25 between 600 and 1000° C.
6. Method according to one of claims 1 to 5, characterized in that it includes a heat exchange step (202) after the gasification step (201) making it possible to cool the synthesis gas to between 4 and 80°C.
7. Method according to claim 6, characterized in that the heat exchange 30 step (202) is carried out before the purification step (204).
8. Method according to one of claims 1 to 7, characterized in that it comprises a dehydration step (203), performed after the heat exchange step (202).
9. Method according to one of claims 1 to 8, characterized in that it is performed at a pressure of 0.5 to 70 bar.
10. Method according to one of claims 1 to 9, characterized in that the 5 temperature of the gas mixture obtained on output from the reactor is between 250 and 700°C.
11. Method according to one of claims 1 to 10, characterized in that the flow obtained after the step of adjustment to specifications is at ambient temperature. 10
12. Device for the production of biomethane from hydrocarbon feedstock, for implementing the method according to claims 1 to 11, comprising at least: - a gasification reactor (10) carrying out a gasification of the feedstock to produce a synthesis gas in a gasification reactor; - a purification unit (16) performing a purification of the synthesis gas 15 produced by the feedstock gasification reactor (10); - a methanation reactor (20) realizing a methanation of the purified synthesis gas; - a means of adjustment to gas specifications (30) of the gas mixture obtained during the synthesis gas methanation step, in order to 20 obtain biomethane; characterized in that the means of adjustment to specifications (30) is designed to recycle a flow comprising at least excess carbon monoxide in the gasification reactor.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FR1160576A FR2982857B1 (en) | 2011-11-21 | 2011-11-21 | PROCESS FOR PRODUCING BIOMETHANE |
FR1160576 | 2011-11-21 | ||
PCT/EP2012/073034 WO2013076051A1 (en) | 2011-11-21 | 2012-11-20 | Biomethane production method |
Publications (2)
Publication Number | Publication Date |
---|---|
NZ626549A NZ626549A (en) | 2015-08-28 |
NZ626549B2 true NZ626549B2 (en) | 2015-12-01 |
Family
ID=
Similar Documents
Publication | Publication Date | Title |
---|---|---|
DK2190950T3 (en) | Method and apparatus for production of liquid biofuel from solid biomass | |
KR101290453B1 (en) | Processes for preparing a catalyzed carbonaceous particulate | |
US8502007B2 (en) | Char methanation catalyst and its use in gasification processes | |
CN102918136A (en) | Method of producing a hydrocarbon composition | |
CN103242134A (en) | Pyrolysis gasification and purification method of household garbage | |
KR101818783B1 (en) | Producing low methane syngas from a two-stage gasifier | |
DK2706103T3 (en) | Process for gasifying a charge of carbonaceous material with improved efficiency | |
AU2012342614B2 (en) | Biomethane production method | |
US8821153B2 (en) | Method and system for the production of a combustible gas from a fuel | |
Hernández et al. | Gasification of grapevine pruning waste in an entrained-flow reactor: gas products, energy efficiency and gas conditioning alternatives | |
NZ626549B2 (en) | Biomethane production method | |
Alamia et al. | Hydrogen from biomass gasification for utilization in oil refineries | |
WO2024059570A1 (en) | Gasification processes and systems for the production of renewable hydrogen |