WO2011159334A1 - Method for producing methane from biomass - Google Patents
Method for producing methane from biomass Download PDFInfo
- Publication number
- WO2011159334A1 WO2011159334A1 PCT/US2011/001048 US2011001048W WO2011159334A1 WO 2011159334 A1 WO2011159334 A1 WO 2011159334A1 US 2011001048 W US2011001048 W US 2011001048W WO 2011159334 A1 WO2011159334 A1 WO 2011159334A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- methane
- hydropyrolysis
- reformer
- char
- catalyst
- Prior art date
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- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims abstract description 146
- 239000002028 Biomass Substances 0.000 title claims abstract description 42
- 238000004519 manufacturing process Methods 0.000 title claims description 4
- 239000003054 catalyst Substances 0.000 claims abstract description 64
- 238000000034 method Methods 0.000 claims abstract description 52
- 239000007789 gas Substances 0.000 claims abstract description 17
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 10
- 239000000203 mixture Substances 0.000 claims abstract description 9
- 230000003635 deoxygenating effect Effects 0.000 claims abstract description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 15
- 229910003294 NiMo Inorganic materials 0.000 claims description 10
- 239000003463 adsorbent Substances 0.000 claims description 9
- 238000006392 deoxygenation reaction Methods 0.000 claims description 6
- 239000002241 glass-ceramic Substances 0.000 claims description 6
- 238000011084 recovery Methods 0.000 claims description 6
- 238000000926 separation method Methods 0.000 claims description 6
- 229910001570 bauxite Inorganic materials 0.000 claims description 4
- 239000008246 gaseous mixture Substances 0.000 claims description 4
- 238000010438 heat treatment Methods 0.000 claims description 4
- 239000012535 impurity Substances 0.000 claims description 4
- NMJORVOYSJLJGU-UHFFFAOYSA-N methane clathrate Chemical compound C.C.C.C.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O.O NMJORVOYSJLJGU-UHFFFAOYSA-N 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 2
- 230000009089 cytolysis Effects 0.000 claims description 2
- 238000002347 injection Methods 0.000 claims description 2
- 239000007924 injection Substances 0.000 claims description 2
- 238000002407 reforming Methods 0.000 claims 2
- 238000002485 combustion reaction Methods 0.000 claims 1
- 239000006112 glass ceramic composition Substances 0.000 claims 1
- 230000005285 magnetism related processes and functions Effects 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 description 28
- 239000000047 product Substances 0.000 description 22
- 238000000197 pyrolysis Methods 0.000 description 13
- 239000002245 particle Substances 0.000 description 10
- 229910052739 hydrogen Inorganic materials 0.000 description 9
- 239000001257 hydrogen Substances 0.000 description 9
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical group [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 7
- 239000000463 material Substances 0.000 description 7
- 229910052717 sulfur Inorganic materials 0.000 description 7
- 239000011593 sulfur Substances 0.000 description 7
- 150000001336 alkenes Chemical class 0.000 description 5
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 5
- 230000015572 biosynthetic process Effects 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 238000001914 filtration Methods 0.000 description 5
- PXHVJJICTQNCMI-UHFFFAOYSA-N nickel Substances [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 241000196324 Embryophyta Species 0.000 description 4
- 238000002309 gasification Methods 0.000 description 4
- 229930195733 hydrocarbon Natural products 0.000 description 4
- 150000002430 hydrocarbons Chemical class 0.000 description 4
- 229910052799 carbon Inorganic materials 0.000 description 3
- 239000000356 contaminant Substances 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 238000011044 inertial separation Methods 0.000 description 3
- 239000003345 natural gas Substances 0.000 description 3
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical class [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 241000195493 Cryptophyta Species 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000004888 barrier function Effects 0.000 description 2
- 229910002090 carbon oxide Inorganic materials 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 238000005367 electrostatic precipitation Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 150000002431 hydrogen Chemical class 0.000 description 2
- 238000005984 hydrogenation reaction Methods 0.000 description 2
- 238000011065 in-situ storage Methods 0.000 description 2
- 150000002632 lipids Chemical class 0.000 description 2
- 238000007885 magnetic separation Methods 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000002574 poison Substances 0.000 description 2
- 231100000614 poison Toxicity 0.000 description 2
- 230000001131 transforming effect Effects 0.000 description 2
- 241001474374 Blennius Species 0.000 description 1
- 241000209499 Lemna Species 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 240000006394 Sorghum bicolor Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000000443 aerosol Substances 0.000 description 1
- 239000012620 biological material Substances 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 239000012065 filter cake Substances 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000012978 lignocellulosic material Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000012263 liquid product Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- FBMUYWXYWIZLNE-UHFFFAOYSA-N nickel phosphide Chemical compound [Ni]=P#[Ni] FBMUYWXYWIZLNE-UHFFFAOYSA-N 0.000 description 1
- -1 offal Substances 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- JTJMJGYZQZDUJJ-UHFFFAOYSA-N phencyclidine Chemical class C1CCCCN1C1(C=2C=CC=CC=2)CCCCC1 JTJMJGYZQZDUJJ-UHFFFAOYSA-N 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000000379 polymerizing effect Effects 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- 238000006057 reforming reaction Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- 238000000629 steam reforming Methods 0.000 description 1
- 239000010907 stover Substances 0.000 description 1
- 229930195735 unsaturated hydrocarbon Natural products 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
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Definitions
- biomass refers to biological material derived from living or deceased organisms and includes lignocellulosic materials, such as wood, aquatic materials, such as algae, aquatic plants, seaweed, and animal by-products and wastes, such as offal, fats, and sewage sludge.
- this invention relates to a multi-stage hydropyrolysis process for producing methane from biomass.
- Gasification is capital intensive because it is run at high temperatures, requires an air separation plant to produce the required oxygen, which air separation plant is capital intensive.
- a multi-stage method and apparatus for producing methane from biomass comprising the steps of hydropyrolizing biomass in a hydropyrolysis reactor vessel containing molecular hydrogen and a deoxygenating catalyst at a hydropyrolysis temperature greater than about 1000°F and a hydropyrolysis pressure in a range of about 100 psig to about 600 psig, producing a hydropyrolysis product comprising char and a gas containing a large proportion of methane, very small quantities of higher hydrocarbons including unsaturated hydrocarbons, but no tar-like material, in addition to H 2 , CO, CO 2 , and H 2 O (steam), and also H 2 S to the extent that there is sulfur in the feedstock, separating the char from the hydropyrolysis product, resulting in a reduced char hydropyrolysis product, and hydroconverting the reduced char hydropyrolysis product in a hydroconversion reactor vessel using a hydroconversion catalyst at a hydroconversion temperature greater than about
- a hydropyrolysis product stream containing substantial amounts of methane is produced.
- the hydroconversion product is cooled and introduced into a water-gas-shift reactor to convert the majority of the CO by reaction with the steam, producing a water-gas-shift product comprising steam and a gaseous mixture comprising CO 2 , H 2 , and methane, but with reduced levels of CO.
- the CO 2 , H 2 , and methane are then separated, producing a CO 2 stream, an H 2 stream, and a methane stream.
- the H 2 is recovered, for example, via a PSA unit, and recycled back to the hydropyrolysis unit.
- the methane stream is then compressed and split between a product gas which is methanated as necessary to remove any residual CO or H 2 or both by conversion to methane, so as to make a methane product acceptable to a pipeline carrying natural gas in the ultimate gas purchase customers thereof, and the rest of the methane is sent to the steam reformer where, after addition of appropriate levels of steam to avoid carbon formation in the catalyst tubes suspended in the furnace box of the reformer, a portion (typically 10-15%) is used as fuel to the furnace box of the reformer, and the rest is steam reformed to make hydrogen for the hydropyrolysis unit.
- a portion of the hydrogen stream from the reformer commensurate to the level of CO, CO 2 , and H 2 entering the methanation unit prior to such hydrogen addition is introduced into the previously mentioned methanation vessel.
- hydrogen reacts with any remaining amounts of carbon oxides (CO 2 and CO) in the methane product stream, forming additional methane and thusly minimizing carbon oxides from the methane product stream.
- Multiple reactors and final stage reactors to attain the desired degree of conversion and to accommodate the heat released by the methanation reactions are provided as necessary as known to those skilled in the art.
- FIG. 1 is a schematic flow diagram of a process for producing methane from biomass in accordance with one embodiment of this invention.
- Fig. 2 is a schematic flow diagram of a process for producing methane in accordance with another embodiment of this invention. DETAILED DESCRIPTION OF THE PRESENTLY
- the process of this invention is a compact, integrated, multi-stage process for thermochemically transforming biomass into methane.
- the first reaction stage or step of this process employs a pressurized, catalytically- enhanced, hydropyrolysis reactor vessel 10 to create a low-char, partially deoxygenated, hydropyrolysis product from which the char is removed.
- a pressurized, catalytically- enhanced, hydropyrolysis reactor vessel 10 to create a low-char, partially deoxygenated, hydropyrolysis product from which the char is removed.
- the preferred reactor vessel is a fluidized bed reactor.
- the hydropyrolysis step employs a rapid heat up in which the average internal temperature of the particle rises at a rate of about
- the residence time of the pyrolysis vapors in the reactor vessel is less than about 1 minute.
- the residence time of the char is relatively long because it is not removed through the bottom of the reactor vessel and, thus, must be reduced in particle size until the aerodynamic diameter of these particles is sufficiently reduced to enable them to be eluted and carried out with the vapors exiting proximate the top of the reactor vessel.
- the second reaction stage (subsequent to char removal) employs a hydroconversion reactor vessel 1 1 in which a hydroconversion step is carried out at substantially the same pressure as the first reaction stage as necessary to convert any olefins to methane.
- the product from the second reaction stage is then sent to a water-gas-shift reactor 12 in which the product is converted to a shift product comprising a mixture of CO 2 , H 2 O, H 2 , and methane and the CO concentration is decreased.
- the shift product is cooled and separated into water, which is used, after water treatment, for steam reforming a portion of the methane product in steam reformer 14, which itself is a component of a packaged reformer-PSA unit 15, and gaseous fractions using high pressure separator 13.
- the mixture of CO 2 , H 2 , and methane is provided to a H 2 recovery unit 16 in which the H 2 is separated from the mixture and combined with H 2 from the packaged reformer-PSA unit.
- the H 2 is then compressed in steam-driven compressor 17 and recycled back to hydropyrolysis reactor vessel 10 for use in the hydropyrolysis process therein.
- the remaining mixture with a small amount of CO and CO 2 is compressed.
- the methane- rich stream leaving the H 2 separation unit 16 may still contain small amounts of CO as an impurity in excess to that allowable for the methane to be acceptable in a natural gas pipeline system.
- a portion of the remaining methane is provided to the methanator 19 in which any residual CO and a portion of the H 2 from the packaged reformer-PSA unit is reacted to produce additional methane.
- a trace sulfur removal system or guard bed may be required to protect the methanation catalyst which is poisoned by sulfur.
- the stream exiting the methanator 19 will be a high-purity methane stream, containing only trace amounts of CO, CO 2 , H 2 , and water vapor. This stream will be dehydrated and compressed to a pressure suitable for admission to the natural gas transmission or other offtake pipeline.
- the remaining portion of methane from H 2 recovery separation unit 16 is sent to the steam reformer 14 together with water as steam for conversion of methane into H 2 and CO 2 .
- a portion of the methane gas is burned in a furnace or other combustor 20 to heat up the remaining portion of methane gas to the operating temperature of the steam reformer, which is about 1700°F. Alternatively, this furnace can be fueled using the char eliminated from the hydropyrolysis product stream downstream of the hydropyrolysis reactor 10.
- a key aspect of this invention is that the heat energy required in the process is supplied by the heat of reaction of the deoxygenation reaction, which is exothermic, occurring in both the first and second stages.
- Another key aspect of this invention is that the biomass feed need not be severely dried and, in fact, the addition of water either in the feed or as a separate feed is advantageous to the process because it enhances in-situ H 2 formation through a water-gas-shift reaction.
- the biomass feed utilized in the process of this invention may be in the form of loose biomass particles having a majority of particles preferably less than about 3mm in size or in the form of a biomass/liquid slurry.
- the biomass feed may be pretreated or otherwise processed in a manner such that larger particle sizes may be accommodated.
- Suitable means for introducing the biomass feed into the hydropyro lysis reactor vessel include, but are not limited to, an auger, fast-moving (greater than about 5m/sec) stream of carrier gas, such as inert or CO 2 gases and H 2 , and constant-displacement pumps, impellers, or turbine pumps.
- Hydropyrolysis is carried out in the reactor vessel at a temperature greater than about 1000°F, preferably in the range of about 1000°F to about 1200°F, and at a pressure in the range of about 100 psig to about 600 psig. Heating rate of the biomass is preferably greater than about 10,000/second.
- the weight hourly space velocity (WHSV) in gm biomass/gm catalyst/hr for this step is in the range of about .2 to about 10.
- the solid biomass feed is rapidly heated, preferably in a hot fluidized bed, resulting in conversion of the biomass to non-char products comparable to and possibly better than yields obtained with conventional fast pyrolysis.
- the hydropyrolysis vapors during hydropyrolysis are in the presence of a catalyst and a high partial pressure of H 2 within the fluidized bed, which provides hydrogenation activity and also some deoxygenation activity. Hydrogenation activity is very desirable for preventing reactive olefins from polymerizing, thereby reducing the formation of unstable free radicals.
- hydropyrolysis avoids the retrograde reactions of pyrolysis, which is usually carried out in an inert atmosphere, most certainly in the absence of H 2 and usually in the absence of a catalyst, thereby promoting the undesirable formation of polynuclear aromatics, free radicals and olefinic compounds that are not present in the original biomass. If hydropyrolysis is carried out at low temperatures, longer-chain molecules will tend to be produced. If hydropyrolysis is carried out at higher temperatures, these molecules will tend to be cracked, producing molecules with shorter carbon chains and increasing the proportion of methane produced during this step.
- the first stage hydropyrolysis step of this invention operates at a temperature hotter than is typical of a conventional hydroconversion process, as a result of which the biomass is rapidly devolatilized.
- the step requires an active catalyst to stabilize the hydropyrolysis vapors, but not so active that the catalyst rapidly cokes.
- Catalyst particle sizes are preferably greater than about 100 micrometers.
- Glass-ceramic catalysts - Glass-ceramic catalysts are extremely strong and attrition resistant and can be prepared as thermally impregnated (i.e. supported) or as bulk catalysts. When employed as a sulfided NiMo, Ni/NiO, CoMo, or Co- based glass-ceramic catalyst, sulfur-active catalyst, the resulting catalyst is an attrition resistant version of a readily available, but soft, conventional NiMo, Ni/NiO, or Co- based catalyst.
- Glass-ceramic sulfided NiMo, Ni/NiO, or Co-based catalysts are particularly suitable for use in a hot fluidized bed because these materials can provide the catalytic effect of a conventional supported catalyst, but in a much more robust, attrition resistant form.
- the biomass and char are simultaneously ground into smaller particles as hydropyrolysis reactions proceed within the reaction vessel.
- the char that is ultimately recovered is substantially free of catalyst contaminants from the catalyst due to the extremely high strength and attrition resistance of the catalyst.
- the attrition rate of the catalyst will typically be less than about 2 weight % per hour, preferably less than 1 weight % per hour as determined in a standard, high velocity jet-cup attrition index test. Catalyst will be added periodically to make up for catalyst losses.
- Nickel phosphide catalyst - Ni Phosphide catalysts do not require sulfur to work, nor are they poisoned by sulfur and therefore will be just as active in a sulfur- free environment as in an environment containing H 2 S, COS and other sulfur- containing compounds. Therefore, this catalyst will be just as active for biomass which has little or no sulfur present as with biomass which does contain sulfur (e.g. corn stover).
- This catalyst may be impregnated on carbon as a separate catalyst or impregnated directly into the biomass feedstock itself.
- Bauxite - Bauxite is an extremely cheap material and, thus, may be used as a disposable catalyst. Bauxite may also be impregnated with other materials such as Ni, Mo, or be sulfided as well.
- NiMo or CoMo catalysts are normally provided as large size 1/8-1/16-inch tablets for use in fixed beds.
- NiMo is impregnated on spray dried silica alumina catalyst and used in a fluidized bed. This catalyst exhibits higher strength than a conventional NiMo or CoMo catalyst and would be of the right size for use in a fluidized bed.
- An alumina support may also serve as a hydropyrolysis catalyst.
- This alumina support could be gamma alumina of an appropriate surface area and size, or have phosphorus disposed upon it as is typical for a hydrotreating catalyst support.
- char is removed from the hydropyrolysis product, typically by inertial separation, such as cyclones, or barrier filtration, such as bayonet filters.
- inertial separation such as cyclones
- barrier filtration such as bayonet filters.
- efficient char removal is made difficult because as char is captured on the surface of a filter, it reacts with the highly-oxygenated hydrocarbon vapors resulting from pyrolysis to create tar-like hydrocarbons that coat and bind the captured char into a dense dust cake that can permanently blind hot process filters.
- the hydrogenated vapors that are produced are non-reactive, low molecular weight hydrocarbons that remain in a gaseous state throughout and pass through a barrier filter without reaction or deposition.
- char may be removed in accordance with the process of this invention by filtration from the vapor stream.
- Backpulsing may be employed in removing char from filters, as long as the hydrogen used in the process of this invention sufficiently hydrogenated and thus reduces the reactivity of the hydropyrolysis vapors leaving the hydropyrolysis reactor.
- Electrostatic precipitation, inertial separation, magnetic separation, or a combination of these technologies may also be used to remove char and ash particles from the hot vapor stream.
- glass-ceramic catalysts are more easily separated from char by energetic inertial separation technologies that typically employ energetic impaction, interception, and/or diffusion processes sometimes combined with electrostatic precipitation to separate, concentrate, and collect char into a secondary stream for recovery.
- energetic inertial separation technologies that typically employ energetic impaction, interception, and/or diffusion processes sometimes combined with electrostatic precipitation to separate, concentrate, and collect char into a secondary stream for recovery.
- electrostatic precipitation to separate, concentrate, and collect char into a secondary stream for recovery.
- An additional virtue of these materials is that, because they are amenable to magnetic separation (in a reduced state, being attracted to a permanent or electrically-induced magnetic field), magnetic techniques as well as combinations of magnetic, inertial, and electrostatic means may be employed for separating char from these catalysts that are not possible with softer materials.
- hot gas filtration may be used to remove the char.
- the dust cake caught on the filters has been found to be more easily cleaned than char removed in the hot filtration of the aerosols produced in conventional fast pyrolysis.
- the hot gas filtration is coupled with injection of suitable adsorbent or mixture of adsorbents for removal of certain impurities.
- the adsorbents form a filter cake on the filter element prior to admission of gas laden with particulates, or in a second, subsequent hot gas filter where the fines/dust particles from hydropyrolysis or hydrogasification have already been removed. Cooling may be provided so as to operate the filter at the optimal conditions which remove a particular contaminant or contaminants with the selected adsorbent or adsorbents.
- Means are provided for pulse blowback of the accumulated adsorbent and/or adsorbent/fines cake buildup on the filter, thereby removing impurities which react at the chosen operating conditions with the adsorbents used.
- the output from the first reaction stage hydropyrolysis step is introduced into a second stage hydroconversion reactor vessel 11 in which it is subjected to a second reaction stage hydroconversion step to convert any olefins to methane.
- This step is preferably carried out at a lower temperature (850-950 °F) than the first reaction stage hydropyrolysis step and at substantially the same pressure (100 - 600 psig) as the first reaction stage hydropyrolysis step.
- the weight hourly space velocity (WHSV) for this step is in the range of about 0.2 to about 3. If the hydroconversion catalyst can be protected from poisons, catalyst life can be expected to be increased.
- the catalyst used in this step should be protected from Na, K, Ca, P, and other metals present in the biomass which can poison the catalyst.
- This catalyst also should be protected from olefins and free radicals by the catalytic upgrading carried out in the hydropyrolysis reactor.
- Catalysts typically selected for this step are high activity hydroconversion catalysts, e.g. sulfided NiMo and sulfided CoMo catalysts.
- the catalyst may be used to catalyze a water-gas-shift reaction of CO + H 2 O to make CO 2 + H 2 , thereby enabling in-situ production of hydrogen, which, in turn, reduces the hydrogen required for hydroconversion.
- NiMo and CoMo catalysts both catalyze the water-gas-shift reaction.
- the biomass feed is an aquatic biomass, possibly containing a high proportion of lipids, such as algae or an aquatic plant low in lipids, such as lemna.
- the integrated process of this invention is ideal for aquatic biomass conversion because it may be carried out on aquatic biomass which is usually only partially dewatered and still capable of producing high quality yields of product gas.
- Fig. 2 shows a further embodiment of the method of this invention in which the output from CO 2 separation unit 18 is provided to a methane hydrate recovery process 25 which produces a pure methane stream and a H 2 stream which may be recycled back to the first stage hydropyrolysis reactor vessel 10.
- a methane hydrate recovery process 25 which produces a pure methane stream and a H 2 stream which may be recycled back to the first stage hydropyrolysis reactor vessel 10.
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- Dispersion Chemistry (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
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Abstract
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Priority Applications (10)
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JP2013515318A JP5847811B2 (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
MX2012014604A MX341104B (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass. |
NZ604743A NZ604743A (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
CN2011800385070A CN103038321A (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
CA2802321A CA2802321C (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
RU2012157780/04A RU2573567C2 (en) | 2010-06-15 | 2011-06-09 | Method of producing methane from biomass |
AU2011265763A AU2011265763B2 (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
EP11796075.7A EP2582778B1 (en) | 2010-06-15 | 2011-06-09 | Method for producing methane from biomass |
BR112012032043A BR112012032043B1 (en) | 2010-06-15 | 2011-06-09 | method for the production of methane from biomass |
UAA201300194A UA112523C2 (en) | 2010-06-15 | 2011-09-06 | METHOD OF OBTAINING BIOMASS METHANE |
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US12/815,743 US8915981B2 (en) | 2009-04-07 | 2010-06-15 | Method for producing methane from biomass |
US12/815,743 | 2010-06-15 |
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EP (1) | EP2582778B1 (en) |
JP (1) | JP5847811B2 (en) |
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CA (1) | CA2802321C (en) |
CL (2) | CL2012003531A1 (en) |
EC (1) | ECSP13012389A (en) |
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Also Published As
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RU2012157780A (en) | 2014-07-20 |
US20100251615A1 (en) | 2010-10-07 |
EP2582778B1 (en) | 2023-06-07 |
ECSP13012389A (en) | 2015-02-28 |
EP2582778A1 (en) | 2013-04-24 |
BR112012032043B1 (en) | 2019-10-22 |
MX2012014604A (en) | 2013-05-06 |
US8915981B2 (en) | 2014-12-23 |
MX341104B (en) | 2016-08-08 |
CA2802321A1 (en) | 2011-12-22 |
BR112012032043A2 (en) | 2016-11-08 |
CN104593024A (en) | 2015-05-06 |
UA112523C2 (en) | 2016-09-26 |
CA2802321C (en) | 2017-01-31 |
CL2012003531A1 (en) | 2013-06-07 |
NZ604743A (en) | 2014-12-24 |
JP2013528688A (en) | 2013-07-11 |
CN110066669A (en) | 2019-07-30 |
RU2573567C2 (en) | 2016-01-20 |
EP2582778C0 (en) | 2023-06-07 |
CN103038321A (en) | 2013-04-10 |
AU2011265763B2 (en) | 2016-07-14 |
JP5847811B2 (en) | 2016-01-27 |
EP2582778A4 (en) | 2014-04-30 |
AU2011265763A1 (en) | 2013-01-10 |
CN110066669B (en) | 2021-03-16 |
CL2017002195A1 (en) | 2018-03-16 |
PE20131059A1 (en) | 2013-09-23 |
MY160418A (en) | 2017-03-15 |
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