US20130145995A1 - Lignin fired supercritical or near critical water generator, system and method - Google Patents

Lignin fired supercritical or near critical water generator, system and method Download PDF

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US20130145995A1
US20130145995A1 US13/437,156 US201213437156A US2013145995A1 US 20130145995 A1 US20130145995 A1 US 20130145995A1 US 201213437156 A US201213437156 A US 201213437156A US 2013145995 A1 US2013145995 A1 US 2013145995A1
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water
lignin
fuel
supercritical
temperature
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Michel Adam Simard
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Renmatix Inc
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Renmatix Inc
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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F22STEAM GENERATION
    • F22BMETHODS OF STEAM GENERATION; STEAM BOILERS
    • F22B1/00Methods of steam generation characterised by form of heating method
    • F22B1/02Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers
    • F22B1/18Methods of steam generation characterised by form of heating method by exploitation of the heat content of hot heat carriers the heat carrier being a hot gas, e.g. waste gas such as exhaust gas of internal-combustion engines
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/04Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/10Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of field or garden waste or biomasses
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/70Blending
    • F23G2201/702Blending with other waste
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2206/00Waste heat recuperation
    • F23G2206/20Waste heat recuperation using the heat in association with another installation
    • F23G2206/203Waste heat recuperation using the heat in association with another installation with a power/heat generating installation
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2207/00Control
    • F23G2207/20Waste supply
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00Special features of, or arrangements for incinerators
    • F23G2900/50206Pelletising waste before combustion
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2900/00Special features of, or arrangements for incinerators
    • F23G2900/55Controlling; Monitoring or measuring
    • F23G2900/55011Detecting the properties of waste to be incinerated, e.g. heating value, density
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste

Definitions

  • the present invention generally relates to devices, systems, and methods of providing recovered lignin of suitable quantity and quality to provide sufficient heating value to power the generation of supercritical or near critical water without the need for outside sources of energy.
  • Processes using hot compressed water may have two distinct operations: pre-treatment and cellulose hydrolysis.
  • the pre-treatment process hydrolyzes the hemicellulose component of the lignocellulosic biomass and cellulose hydrolysis (CH) process, as its name infers, hydrolyzes the cellulose fibers.
  • CH cellulose hydrolysis
  • the resultant five carbon (C5) and six carbon (C6) sugar streams are recovered separately.
  • the remaining solids, which consist mostly of lignin, are preferably recovered, such as through filtration, and may be used as a fuel to provide thermal energy to the process itself or for other processes.
  • the CH process uses a significant amount of supercritical water (T>373° C., P>3,206 psi).
  • the SCW must be generated in a heater at high pressure and pumped into the process.
  • lignin of suitable quantity and quality could be recovered during the process to provide sufficient heating value to power the generation of SCW without the need for outside sources of energy.
  • the methods, devices, and systems of the present invention are directed toward these, as well as other, important ends.
  • the invention is directed to methods of generating supercritical or near critical water, comprising:
  • heating comprises combusting a fuel composition comprising lignin
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • the invention is directed to methods of generating supercritical or near critical water, comprising:
  • heating comprises combusting a fuel composition comprising lignin
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • the invention is directed to supercritical or near critical water generators, comprising:
  • At least one pump adapted to provide water at a pressure of at least about 221 bar to form compressed water
  • At least one fuel combustion apparatus adapted for combusting a fuel composition comprising lignin
  • lignin is generated in a process wherein said supercritical or near critical water generator is employed;
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865;
  • the invention is directed to systems for generating supercritical or near critical water, comprising:
  • a fuel handling system adapted to transport said fuel composition to said fuel combustion apparatus
  • a water circulation system adapted to transport said compressed water in proximity of said fuel combustion apparatus adequate to heat said compressed water to a temperature of at least about 373° C. to produce said supercritical or near critical water;
  • FIG. 1 is a block flow diagram of a supercritical or near critical water generator device of one embodiment of the invention.
  • FIG. 2 is a schematic diagram of a solid fuel burner of one embodiment of the invention.
  • the phrase “substantially free” means have no more than about 1%, preferably less than about 0.5%, more preferably, less than about 0.1%, by weight of a component, based on the total weight of any composition containing the component.
  • a supercritical fluid is a fluid at a temperature above its critical temperature and at a pressure above its critical pressure.
  • a supercritical fluid exists at or above its “critical point,” the point of highest temperature and pressure at which the liquid and vapor (gas) phases can exist in equilibrium with one another. Above critical pressure and critical temperature, the distinction between liquid and gas phases disappears.
  • a supercritical fluid possesses approximately the penetration properties of a gas simultaneously with the solvent properties of a liquid. Accordingly, supercritical fluid extraction has the benefit of high penetrability and good solvation.
  • Reported critical temperatures and pressures include: for pure water, a critical temperature of about 374.2° C., and a critical pressure of about 221 bar; for carbon dioxide, a critical temperature of about 31° C. and a critical pressure of about 72.9 atmospheres (about 1072 psig).
  • Near critical water has a temperature at or above about 300° C. and below the critical temperature of water (374.2° C.), and a pressure high enough to ensure that all fluid is in the liquid phase.
  • Sub-critical water has a temperature of less than about 300° C. and a pressure high enough to ensure that all fluid is in the liquid phase.
  • Sub-critical water temperature may be greater than about 250° C. and less than about 300° C., and in many instances sub-critical water has a temperature between about 250° C.
  • hot compressed water is used interchangeably herein for water that is at or above its critical state, or defined herein as near-critical or sub-critical, or any other temperature above about 50° C. (preferably, at least about 100° C.) but less than subcritical and at pressures such that water is in a liquid state
  • a fluid which is “supercritical” indicates a fluid which would be supercritical if present in pure form under a given set of temperature and pressure conditions.
  • “supercritical water” indicates water present at a temperature of at least about 374.2° C. and a pressure of at least about 221 bar, whether the water is pure water, or present as a mixture (e.g. water and ethanol, water and CO 2 , etc.).
  • a mixture of sub-critical water and supercritical carbon dioxide indicates a mixture of water and carbon dioxide at a temperature and pressure above that of the critical point for carbon dioxide but below the critical point for water, regardless of whether the supercritical phase contains water and regardless of whether the water phase contains any carbon dioxide.
  • a mixture of sub-critical water and supercritical CO 2 may have a temperature of about 250° C. to about 280° C. and a pressure of at least about 225 bar.
  • lignocellulosic biomass or a component part thereof refers to plant biomass containing cellulose, hemicellulose, and lignin from a variety of sources, including, without limitation (1) agricultural residues (including corn stover and sugarcane bagasse), (2) dedicated energy crops, (3) wood residues (including hardwoods, softwoods, sawmill and paper mill discards), and (4) municipal waste, and their constituent parts including without limitation, lignocellulose biomass itself, lignin, C 6 saccharides (including cellulose, cellobiose, C 6 oligosaccharides, C 6 monosaccharides, C 5 saccharides (including hemicellulose, C 5 oligosaccharides, and C 5 monosaccharides), and mixtures thereof.
  • agricultural residues including corn stover and sugarcane bagasse
  • wood residues including hardwoods, softwoods, sawmill and paper mill discards
  • municipal waste and their constituent parts including without limitation, lignocellulose biomass itself, lignin, C 6 saccharides (including cellulose
  • the invention is directed to methods of generating supercritical or near critical water, comprising:
  • heating comprises combusting a fuel composition comprising lignin
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • the invention is directed to methods of generating supercritical or near critical water, comprising:
  • heating comprises combusting a fuel composition comprising lignin
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • FIG. 1 A block flow diagram of one embodiment of the invention, where the supercritical water generator 15 in a system, is shown in FIG. 1 :
  • Fresh water 1 a is pumped using a high pressure pump 18 to a minimum pressure of 221 bar.
  • the pressurized fresh water 1 b is optionally pre-heated with a heat exchanger 20 to reduce fuel costs, if other process heat is available (such as process-recovered heat stream 19 ).
  • the pre-heated water 2 then enters the firebox 24 of the supercritical water generator 15 , where it is heated by the combustion of lignin fuel in a fuel combustion apparatus (burner assembly) 21 , preferably generated by the process itself.
  • Water 3 exits the generator 15 at supercritical or near critical conditions.
  • Combustion gases 9 exit the firebox through a flue or chimney (not shown), and are typically subject to pollution control equipment 12 a before exiting to the atmosphere.
  • the ash 10 (residue from solid fuel) is removed from the burner and firebox at the bottom of the supercritical water generator 15 .
  • the system includes a supercritical or near-critical water generator 15 , a fuel handling system 22 adapted to transport lignin fuel to the fuel combustion apparatus (burner assembly) 21 , and a water circulation system 23 adapted to transport said fresh water 1 a to the supercritical water generator 15 to heat said fresh water to a temperature of at least about 373° C. to produce said supercritical or near critical water 3 .
  • the water supply system typically consists of a water source, filter, storage tank and transfer pump. Water is typically filtered, dechlorinated or otherwise demineralized by a filter. This filtered water is store in a storage tank. The filtered water is transferred from the storage tank to the supercritical water generator by means of a pump or gravity, and serves as fresh water to the supercritical water generator.
  • the lignin (wet) 4 may be stored in bulk storage 11 (or alternatively, in, piles, silos or similar manner), where it can accumulate moisture depending upon the storage conditions. It may be conveyed into an optional drying system 13 to remove the excess moisture.
  • the dryer can be powered by steam 17 , in which case condensate 16 would be recovered, but can also in other embodiments be powered by electricity or other heat sources.
  • the dried lignin fuel 5 may then be combusted. At this stage, the moisture content is typically about 25% to about 35%, but may be as low as about 10%.
  • the moisture that is driven off during the drying process may be vented to the atmosphere 8 . This vent may require pollution control equipment 12 b depending on the VOC content of the gases.
  • the air 6 required for combustion is optionally pre-heated in an air exchanger 14 to form pre-heated combustion air 7 , by the flue gases 9 that leave the firebox 24 .
  • the pre-heated air 7 is then mixed with the dried lignin fuel 5 , in the burner assembly 21 and ignited.
  • system includes the following:
  • Inputs wet solid fuel (lignin), LP steam (optional, if drying desired only)
  • Outputs dry fuel (lignin), condensate (from steam), air emission through vent
  • Input water (from river, city, well, etc.)
  • Output filtered or treated water (also referred to herein as “fresh water”)
  • the methods of the invention may be carried out as continuous processes, semi-batch processes, or batch processes.
  • the heating and pressurizing steps may be carried out sequentially or simultaneously or a combination of both.
  • the heating step comprises combusting lignin having heating value of at least about 5,000 BTU/lb, preferably at least about 7,500 BTU/lb, and even more preferably, about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • the fuel composition produces less than about 20%, by weight, based on the weight of the fuel composition, of ash, when combusted. In certain embodiments, the fuel composition produces less than about 10%, by weight, based on the weight of the fuel composition, of ash, when combusted.
  • the method optionally comprises drying the fuel composition comprising the lignin prior to combustion.
  • the moisture content of the fuel composition comprising the lignin is less than about 50% by weight, based on the total weight of the fuel composition, more preferably less than about 35% by weight, based on the total weight of the fuel composition, even more preferably less that about 25% by weight, based on the total weight of the fuel composition, and yet even more preferably less than about 10% by weight, based on the total weight of the fuel composition.
  • the lignin is in a powdered form. In other embodiments, the lignin is in a pelletized form. In yet other embodiments, the lignin is in a liquid form. Furthermore, the lignin may be in a combination of different forms (powdered, pelletized, and/or liquid form).
  • the lignin is produced from a material comprising lignocellulose, such as lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover, and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), municipal paper waste, and combinations thereof.
  • lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover, and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), municipal paper waste, and combinations thereof.
  • the water in said providing step is at about ambient pressure and about ambient temperature.
  • the water in said providing step is clean water, i.e., it is substantially free of impurities, such as, for example, inorganic compounds like chlorine, calcium, metals, and the like, and organic compounds.
  • impurities such as, for example, inorganic compounds like chlorine, calcium, metals, and the like, and organic compounds.
  • suitable clean water is deionized water or typical feed water used for industrial boilers.
  • the fuel composition used in the methods of the invention further comprises at least one supplemental fuel, such as, for example, biomass (including lignocellulosic biomass and component parts thereof and non-lignocellulosic biomass), natural gas, coal (especially coal particulate), and mixtures thereof.
  • biomass including lignocellulosic biomass and component parts thereof and non-lignocellulosic biomass
  • natural gas especially coal particulate
  • mixtures thereof for example, in certain embodiments, tree bark may be co-fired with the lignin. Particulate forms of each of the solid supplemental fuels are preferred for handling reasons.
  • the methods further comprise the step of preheating said water or said compressed water prior to said step of heating.
  • the water or said compressed water is preheated to a temperature of about 100° C. and about 300° C.
  • the heating step is carried out as multiple steps.
  • the pressurizing step is carried out as multiple steps.
  • the lignin has heating value of at least about 5,000 BTU/lb, preferably, at least about 7,500 BTU/lb, even more preferably about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • the fuel composition comprising lignin is in a powdered form, including both wet and dry powders. In certain embodiments, the fuel composition comprising lignin is in a pelletized form, including both wet and dry pellets. In certain embodiments, the fuel composition comprising lignin is in a liquid form. In certain embodiments, the fuel composition comprising lignin is a combination of powdered form, pelletized form, and/or liquid form.
  • the lignin is produced from a material comprising lignocellulose, such as lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), and municipal paper waste and various combinations thereof.
  • lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), and municipal paper waste and various combinations thereof.
  • the invention is directed to supercritical or near critical water generators.
  • Such generators heat water up to and above the critical point of water to create supercritical water or near critical water, as needed.
  • Such devices comprise:
  • At least one pump (such as the pump adapted to provide water at a pressure of at least about 221 bar to form compressed water;
  • At least one fuel combustion apparatus (such as a burner, as shown in FIG. 1 ) adapted for combusting a fuel composition comprising lignin;
  • lignin is generated in a process wherein said supercritical or near critical water generator is employed;
  • said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865;
  • the supercritical or near critical water generator further comprises at least one dryer for said fuel composition comprising lignin.
  • the invention is directed to systems for generating supercritical or near critical water, comprising:
  • a fuel handling system adapted to transport said fuel composition to said fuel combustion apparatus
  • a water circulation system adapted to transport said compressed water in proximity of said fuel combustion apparatus adequate to heat said compressed water to a temperature of at least about 373° C. to produce said supercritical or near critical water;
  • the fuel combustion apparatus adapted for combusting a fuel composition comprising lignin having a heating value of at least about 5,000 BTU/lb, preferably, at least about 7,500 BTU/lb, and even more preferably about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • the fuel handling system is adapted to transport said fuel comprising lignin, wherein said lignin is in a powdered form, including both wet and dry powders. In certain embodiments, the fuel handling system is adapted to transport said fuel comprising lignin, wherein said lignin is in a pelletized form, including both wet and dry pellets. In certain embodiments, the fuel handling system is adapted to transport said fuel composition comprising lignin, wherein said lignin is in a liquid form. In certain other embodiments, the fuel handling system is adapted to transport said fuel composition comprising lignin, wherein said lignin is a combination of powdered form, pelletized form, and/or liquid form.
  • the system further comprises at least one preheater for said water or said compressed water in association with said water circulation system.
  • the preheater heats said water or said compressed water to a temperature of about 100° C. and about 300° C.
  • a lignin-fired SCW generator useful in the methods and systems may be used at the commercial scale at a feed rate of about 1000 dry tons/day of biomass. Based on modeling, the heat requirement equals approximately 200 MMBTU/hr.
  • a suitable range of conditions for the lignin-fired SCW generator of the invention is shown in Table 1.
  • the SCW generator needs to be capable of producing sub-critical and supercritical water at the conditions shown in Table 1 above.
  • the generator should utilize as its primary fuel the process-derived lignin with natural gas as secondary/backup.
  • the generator should also be capable of about 25% turn down, i.e., from 100% to 75% operating capacity.
  • the process derived lignin exits the process at a moisture content (MC) between about 50% and about 60%.
  • MC moisture content
  • Lignin above 35% MC may be difficult to combust, so some form of drying is preferred.
  • the simplest method of drying is taking the lignin from the process separator and air dry it in a covered pile that is turned frequently for several days. Alternatively, excess process heat may be used to facilitate drying and shorten the drying cycle time.
  • the high heating value, % volatile material, ash content, and ash fusion temperature are all important characteristics to monitor.
  • the lignin upon drying, agglomerates to a particle size of approximately 60 mesh. The material is easily crumbled further, so no additional size reduction is anticipated. If a secondary biomass fuel, such as bark, is to be utilized, it is size reduced to the approximate lignin size and well mixed prior to combustion.
  • the burner is capable of handling 50% excess air. This parameter may drop to about 15% if the lignin moisture content also dropped to about 15% to about 20%.
  • the air is not expected to require any preheating or conditioning.
  • the combustion air is blown in with the lignin through the burner. Excess air is supplied as either under fired, over fired, or a combination of under and over fired, again with blowers.
  • the generator preferably has the capability of supplying both. In addition to ambient air as the oxidant, pure oxygen (O 2 ) would also work, but is not preferred due to cost.
  • pretreatment may include carbon filtration, softening, and membrane separation through a reverse osmosis (RO) unit.
  • the SCW feed may be pumped to pressure (about 4,100 psi (283 bar)) then optionally preheated (by a process heat recovery exchanger) to about 392° F. (200° C.) just prior to entering the generator.
  • the burner 34 may be of typical design with a center feed port 35 for solid fuel surrounded by concentric forced air ports 36 and secondary fuel ports 37 , such as shown in FIG. 2 :
  • the solid fuel port may be at least about 4′′ in diameter, preferably about 6′′ to about 8′′ and about 4′ to about 6′ long, made of carbon steel, with enough flow to push flame temperature away from the burner end.
  • the ports may be swirled to discharge fuel in a helical pattern within the firebox for increased travel length and burn time allowing for more complete combustion. Flame temperature preferably do not decrease significantly with turn down
  • the size of the chamber may be about 40′ long and combined with the heat transfer section be about 30′ high. Ceramic refractory may be used for lining the chamber. As with any solid fuel, soot collecting on the outside of the tubes and within the firebox is a consideration. Allowance is made for pressure washing and/or the installation of soot blowers to minimize this fouling.
  • the process coil may be positioned above the burner firebox in a position to allow cross flow of the heated flue gas. In certain embodiments, it may be serpentine with 180° bends and seamlessly finned to enhance convective heat transfer.
  • the coil may include about 1′′ to about 2′′ outside diameter tubes of stainless steel.
  • Stainless steel (SAE 316L) is a suitable material of construction; however, because of the high pressure and possible sulfur impacts from the lignin, the material of construction may preferably include Inconel.
  • the flue gas should be no cooler than about 550° F. (288° C.) to avoid acid gas dew point issues and the accompanying corrosion concerns for the exhaust ducts and stack. Higher temperatures would allow for a smaller coil.
  • a rotary valve with drag chain conveyor (or equivalent) may be incorporated for ash handling.
  • SCW Supercritical Water
  • NCW Near-Critical Water
  • the SCW or NCW is utilized as a “once through” utility. In other embodiments, the SCW or NCW may be recovered, treated, and reused.
  • the SCW or NCW generator it is of a transportable scale with two complete coil assemblies per generator. Splitting into two assemblies also minimizes the field erection and welding concerns allowing much of the welding to be performed at the shop versus in the field.
  • the SCW or NCW generator may be cold/warm started with water. Either natural gas or lignin may be used as the startup fuel with the possibility of using other biomass fuels if sized appropriately. Heat up of the unit is preferably slow and steady to avoid building up heat stresses at the entrances to the generator, the locations where the greatest temperature differentials exist.
  • the generator never goes cold, but maintains a certain (warm) temperature in the firebox. Cold restarts create large heat stresses that can damage the generator.
  • lignin as a fuel minimizes process operating costs and optimizes the overall process two-fold: it removes a large solid waste stream that would otherwise have to be disposed of and it minimizes the amount of fossil fuels combusted thus minimizing greenhouse gas emissions.

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Abstract

Methods are disclosed for providing recovered lignin of suitable quantity and quality to provide sufficient heating value to power the generation of supercritical or near critical water without the need for outside sources of energy. Supercritical or near critical water generator devices and systems are also disclosed.

Description

    CROSS REFERENCE TO RELATED APPLICATIONS
  • This application claims the benefit of U.S. Application No. 61/569,851, filed Dec. 13, 2011, the entire disclosure of which is incorporated herein by reference.
  • FIELD OF THE INVENTION
  • The present invention generally relates to devices, systems, and methods of providing recovered lignin of suitable quantity and quality to provide sufficient heating value to power the generation of supercritical or near critical water without the need for outside sources of energy.
  • BACKGROUND OF THE INVENTION
  • There are a number of processes for converting lignocellulosic biomass into liquid streams of various sugars. Certain preferred processes are based on supercritical water (SCW) or hot compressed water (HCW) technology, which offer several advantages including high throughputs, use of mixed feedstocks, separation of sugars, and avoidance of concentrated acids, microbial cultures, and enzymes. Processes using hot compressed water may have two distinct operations: pre-treatment and cellulose hydrolysis. The pre-treatment process hydrolyzes the hemicellulose component of the lignocellulosic biomass and cellulose hydrolysis (CH) process, as its name infers, hydrolyzes the cellulose fibers. The resultant five carbon (C5) and six carbon (C6) sugar streams are recovered separately. The remaining solids, which consist mostly of lignin, are preferably recovered, such as through filtration, and may be used as a fuel to provide thermal energy to the process itself or for other processes.
  • The CH process uses a significant amount of supercritical water (T>373° C., P>3,206 psi). Generally, the SCW must be generated in a heater at high pressure and pumped into the process. Ideally, lignin of suitable quantity and quality could be recovered during the process to provide sufficient heating value to power the generation of SCW without the need for outside sources of energy. The methods, devices, and systems of the present invention are directed toward these, as well as other, important ends.
  • SUMMARY OF THE INVENTION
  • In one embodiment, the invention is directed to methods of generating supercritical or near critical water, comprising:
  • providing water;
  • applying to said water a pressure of at least about 221 bar to form compressed water; and
  • heating said compressed water to a temperature of at least about 373° C.;
  • wherein said heating comprises combusting a fuel composition comprising lignin; and
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • In another embodiment, the invention is directed to methods of generating supercritical or near critical water, comprising:
  • providing water;
  • heating said water to a temperature of at least about 373° C. to form superheated steam;
  • applying to said superheated steam a pressure of at least about 221 bar;
  • wherein said heating comprises combusting a fuel composition comprising lignin; and
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • In certain aspects, the invention is directed to supercritical or near critical water generators, comprising:
  • at least one pump adapted to provide water at a pressure of at least about 221 bar to form compressed water;
  • at least one fuel combustion apparatus adapted for combusting a fuel composition comprising lignin;
  • wherein said lignin is generated in a process wherein said supercritical or near critical water generator is employed;
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865; and
  • optional controls.
  • In certain aspects, the invention is directed to systems for generating supercritical or near critical water, comprising:
  • a supercritical or near critical water generator described herein;
  • a fuel handling system adapted to transport said fuel composition to said fuel combustion apparatus;
  • a water circulation system adapted to transport said compressed water in proximity of said fuel combustion apparatus adequate to heat said compressed water to a temperature of at least about 373° C. to produce said supercritical or near critical water; and
  • optional controls.
  • BRIEF DESCRIPTION OF THE DRAWINGS
  • The accompanying drawings, which are included to provide a further understanding of the invention and are incorporated in and constitute a part of this specification, illustrate embodiments of the invention and together with the description serve to explain the principles of the invention. In the drawings:
  • FIG. 1 is a block flow diagram of a supercritical or near critical water generator device of one embodiment of the invention.
  • FIG. 2 is a schematic diagram of a solid fuel burner of one embodiment of the invention.
  • DETAILED DESCRIPTION OF THE INVENTION
  • As employed above and throughout the disclosure, the following terms, unless otherwise indicated, shall be understood to have the following meanings
  • As used herein, the singular forms “a,” “an,” and “the” include the plural reference unless the context clearly indicates otherwise.
  • While the present invention is capable of being embodied in various forms, the description below of several embodiments is made with the understanding that the present disclosure is to be considered as an exemplification of the invention, and is not intended to limit the invention to the specific embodiments illustrated. Headings are provided for convenience only and are not to be construed to limit the invention in any manner. Embodiments illustrated under any heading may be combined with embodiments illustrated under any other heading.
  • The use of numerical values in the various quantitative values specified in this application, unless expressly indicated otherwise, are stated as approximations as though the minimum and maximum values within the stated ranges were both preceded by the word “about.” In this manner, slight variations from a stated value can be used to achieve substantially the same results as the stated value. Also, the disclosure of ranges is intended as a continuous range including every value between the minimum and maximum values recited as well as any ranges that can be formed by such values. Also disclosed herein are any and all ratios (and ranges of any such ratios) that can be formed by dividing a recited numeric value into any other recited numeric value. Accordingly, the skilled person will appreciate that many such ratios, ranges, and ranges of ratios can be unambiguously derived from the numerical values presented herein and in all instances such ratios, ranges, and ranges of ratios represent various embodiments of the present invention.
  • As used herein, the phrase “substantially free” means have no more than about 1%, preferably less than about 0.5%, more preferably, less than about 0.1%, by weight of a component, based on the total weight of any composition containing the component.
  • A supercritical fluid is a fluid at a temperature above its critical temperature and at a pressure above its critical pressure. A supercritical fluid exists at or above its “critical point,” the point of highest temperature and pressure at which the liquid and vapor (gas) phases can exist in equilibrium with one another. Above critical pressure and critical temperature, the distinction between liquid and gas phases disappears. A supercritical fluid possesses approximately the penetration properties of a gas simultaneously with the solvent properties of a liquid. Accordingly, supercritical fluid extraction has the benefit of high penetrability and good solvation.
  • Reported critical temperatures and pressures include: for pure water, a critical temperature of about 374.2° C., and a critical pressure of about 221 bar; for carbon dioxide, a critical temperature of about 31° C. and a critical pressure of about 72.9 atmospheres (about 1072 psig). Near critical water has a temperature at or above about 300° C. and below the critical temperature of water (374.2° C.), and a pressure high enough to ensure that all fluid is in the liquid phase. Sub-critical water has a temperature of less than about 300° C. and a pressure high enough to ensure that all fluid is in the liquid phase. Sub-critical water temperature may be greater than about 250° C. and less than about 300° C., and in many instances sub-critical water has a temperature between about 250° C. and about 280° C. The term “hot compressed water” is used interchangeably herein for water that is at or above its critical state, or defined herein as near-critical or sub-critical, or any other temperature above about 50° C. (preferably, at least about 100° C.) but less than subcritical and at pressures such that water is in a liquid state
  • As used herein, a fluid which is “supercritical” (e.g. supercritical water, supercritical CO2, etc.) indicates a fluid which would be supercritical if present in pure form under a given set of temperature and pressure conditions. For example, “supercritical water” indicates water present at a temperature of at least about 374.2° C. and a pressure of at least about 221 bar, whether the water is pure water, or present as a mixture (e.g. water and ethanol, water and CO2, etc.). Thus, for example, “a mixture of sub-critical water and supercritical carbon dioxide” indicates a mixture of water and carbon dioxide at a temperature and pressure above that of the critical point for carbon dioxide but below the critical point for water, regardless of whether the supercritical phase contains water and regardless of whether the water phase contains any carbon dioxide. For example, a mixture of sub-critical water and supercritical CO2 may have a temperature of about 250° C. to about 280° C. and a pressure of at least about 225 bar.
  • As used herein, “lignocellulosic biomass or a component part thereof” refers to plant biomass containing cellulose, hemicellulose, and lignin from a variety of sources, including, without limitation (1) agricultural residues (including corn stover and sugarcane bagasse), (2) dedicated energy crops, (3) wood residues (including hardwoods, softwoods, sawmill and paper mill discards), and (4) municipal waste, and their constituent parts including without limitation, lignocellulose biomass itself, lignin, C6 saccharides (including cellulose, cellobiose, C6 oligosaccharides, C6 monosaccharides, C5 saccharides (including hemicellulose, C5 oligosaccharides, and C5 monosaccharides), and mixtures thereof.
  • Accordingly, in one embodiment, the invention is directed to methods of generating supercritical or near critical water, comprising:
  • providing water;
  • applying to said water a pressure of at least about 221 bar to form compressed water; and
  • heating said compressed water to a temperature of at least about 373° C.;
  • wherein said heating comprises combusting a fuel composition comprising lignin; and
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • In another embodiment, the invention is directed to methods of generating supercritical or near critical water, comprising:
  • providing water;
  • heating said water to a temperature of at least about 373° C. to form superheated steam;
  • applying to said superheated steam a pressure of at least about 221 bar;
  • wherein said heating comprises combusting a fuel composition comprising lignin; and
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865.
  • A block flow diagram of one embodiment of the invention, where the supercritical water generator 15 in a system, is shown in FIG. 1:
    • 1 a Fresh water
    • 1 b Pressurized, fresh water
    • 2 Pre-heated water
    • 3 Supercritical water (SCW)
    • 4 Lignin (wet)
    • 5 Lignin (dry)
    • 6 Air
    • 7 Preheated combustion air
    • 8 Vent to atmosphere
    • 9 Flue or combustion gas
    • 10 Ash
    • 11 Lignin storage
    • 12 a Air pollution control
    • 12 b Air pollution control
    • 13 Dryer (optional)
    • 14 Air exchanger (optional)
    • 15 SCW generator
    • 16 Condensate
    • 17 Low pressure steam
    • 18 High pressure pump
    • 19 Process-recovered heat stream (optional)
    • 20 Heat exchanger (optional)
    • 21 Fuel combustion apparatus (burner assembly)
    • 22 Fuel handling system
    • 23 Water handling system
    • 24 Firebox
    • 25 Water tank
    • 26 Water transfer pump
    • 27 Filter
    • 28 Incoming water
  • Fresh water 1 a is pumped using a high pressure pump 18 to a minimum pressure of 221 bar. The pressurized fresh water 1 b is optionally pre-heated with a heat exchanger 20 to reduce fuel costs, if other process heat is available (such as process-recovered heat stream 19). The pre-heated water 2 then enters the firebox 24 of the supercritical water generator 15, where it is heated by the combustion of lignin fuel in a fuel combustion apparatus (burner assembly) 21, preferably generated by the process itself. Water 3 exits the generator 15 at supercritical or near critical conditions. Combustion gases 9 exit the firebox through a flue or chimney (not shown), and are typically subject to pollution control equipment 12 a before exiting to the atmosphere. The ash 10 (residue from solid fuel) is removed from the burner and firebox at the bottom of the supercritical water generator 15.
  • The system includes a supercritical or near-critical water generator 15, a fuel handling system 22 adapted to transport lignin fuel to the fuel combustion apparatus (burner assembly) 21, and a water circulation system 23 adapted to transport said fresh water 1 a to the supercritical water generator 15 to heat said fresh water to a temperature of at least about 373° C. to produce said supercritical or near critical water 3.
  • The water supply system typically consists of a water source, filter, storage tank and transfer pump. Water is typically filtered, dechlorinated or otherwise demineralized by a filter. This filtered water is store in a storage tank. The filtered water is transferred from the storage tank to the supercritical water generator by means of a pump or gravity, and serves as fresh water to the supercritical water generator.
  • The lignin (wet) 4 may be stored in bulk storage 11 (or alternatively, in, piles, silos or similar manner), where it can accumulate moisture depending upon the storage conditions. It may be conveyed into an optional drying system 13 to remove the excess moisture. The dryer can be powered by steam 17, in which case condensate 16 would be recovered, but can also in other embodiments be powered by electricity or other heat sources. The dried lignin fuel 5 may then be combusted. At this stage, the moisture content is typically about 25% to about 35%, but may be as low as about 10%. The moisture that is driven off during the drying process may be vented to the atmosphere 8. This vent may require pollution control equipment 12 b depending on the VOC content of the gases.
  • The air 6 required for combustion is optionally pre-heated in an air exchanger 14 to form pre-heated combustion air 7, by the flue gases 9 that leave the firebox 24. The pre-heated air 7 is then mixed with the dried lignin fuel 5, in the burner assembly 21 and ignited.
  • In another embodiment of the invention, system includes the following:
  • Fuel Handling System:
  • a. Inputs: wet solid fuel (lignin), LP steam (optional, if drying desired only)
    b. Outputs: dry fuel (lignin), condensate (from steam), air emission through vent
  • Water Circulation System:
  • a. Input: water (from river, city, well, etc.)
    b. Output: filtered or treated water (also referred to herein as “fresh water”)
  • SCW Generator:
  • a. Inputs: dry fuel (lignin), fresh water, combustion air
    b. Outputs: SCW, ash, air emission
  • The methods of the invention may be carried out as continuous processes, semi-batch processes, or batch processes. In certain embodiments of batch and semi-batch processes, the heating and pressurizing steps may be carried out sequentially or simultaneously or a combination of both.
  • In certain embodiments, the heating step comprises combusting lignin having heating value of at least about 5,000 BTU/lb, preferably at least about 7,500 BTU/lb, and even more preferably, about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • In certain embodiments, the fuel composition produces less than about 20%, by weight, based on the weight of the fuel composition, of ash, when combusted. In certain embodiments, the fuel composition produces less than about 10%, by weight, based on the weight of the fuel composition, of ash, when combusted.
  • In certain embodiments, the method optionally comprises drying the fuel composition comprising the lignin prior to combustion. Preferably, the moisture content of the fuel composition comprising the lignin is less than about 50% by weight, based on the total weight of the fuel composition, more preferably less than about 35% by weight, based on the total weight of the fuel composition, even more preferably less that about 25% by weight, based on the total weight of the fuel composition, and yet even more preferably less than about 10% by weight, based on the total weight of the fuel composition.
  • In certain embodiments, the lignin is in a powdered form. In other embodiments, the lignin is in a pelletized form. In yet other embodiments, the lignin is in a liquid form. Furthermore, the lignin may be in a combination of different forms (powdered, pelletized, and/or liquid form).
  • In certain embodiments, the lignin is produced from a material comprising lignocellulose, such as lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover, and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), municipal paper waste, and combinations thereof.
  • In certain embodiments, the water in said providing step is at about ambient pressure and about ambient temperature.
  • In certain embodiments, the water in said providing step is clean water, i.e., it is substantially free of impurities, such as, for example, inorganic compounds like chlorine, calcium, metals, and the like, and organic compounds. An example of suitable clean water is deionized water or typical feed water used for industrial boilers.
  • In certain embodiments, the fuel composition used in the methods of the invention further comprises at least one supplemental fuel, such as, for example, biomass (including lignocellulosic biomass and component parts thereof and non-lignocellulosic biomass), natural gas, coal (especially coal particulate), and mixtures thereof. For example, in certain embodiments, tree bark may be co-fired with the lignin. Particulate forms of each of the solid supplemental fuels are preferred for handling reasons.
  • In certain embodiments, the methods further comprise the step of preheating said water or said compressed water prior to said step of heating. In certain preferred embodiments, the water or said compressed water is preheated to a temperature of about 100° C. and about 300° C.
  • In certain embodiments, the heating step is carried out as multiple steps.
  • In certain embodiments, the pressurizing step is carried out as multiple steps.
  • In certain embodiments, the lignin has heating value of at least about 5,000 BTU/lb, preferably, at least about 7,500 BTU/lb, even more preferably about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • In certain embodiments, the fuel composition comprising lignin is in a powdered form, including both wet and dry powders. In certain embodiments, the fuel composition comprising lignin is in a pelletized form, including both wet and dry pellets. In certain embodiments, the fuel composition comprising lignin is in a liquid form. In certain embodiments, the fuel composition comprising lignin is a combination of powdered form, pelletized form, and/or liquid form.
  • In certain embodiments, the lignin is produced from a material comprising lignocellulose, such as lignocellulose biomass obtained from a wide variety of sources including, but not limited to, agricultural residues (including straw, corn stover and sugarcane bagasse), dedicated energy crops, wood residues (including hardwoods, softwoods, and sawmill and paper mill discards), and municipal paper waste and various combinations thereof.
  • In certain aspects, the invention is directed to supercritical or near critical water generators. Such generators heat water up to and above the critical point of water to create supercritical water or near critical water, as needed. Such devices comprise:
  • at least one pump (such as the pump adapted to provide water at a pressure of at least about 221 bar to form compressed water;
  • at least one fuel combustion apparatus (such as a burner, as shown in FIG. 1) adapted for combusting a fuel composition comprising lignin;
  • wherein said lignin is generated in a process wherein said supercritical or near critical water generator is employed;
  • wherein said lignin has a heating value of at least about 3,000 BTU/lb, as measured by ASTM-D240 or D5865; and
  • optional controls.
  • In certain embodiments, the supercritical or near critical water generator further comprises at least one dryer for said fuel composition comprising lignin.
  • In certain aspects, the invention is directed to systems for generating supercritical or near critical water, comprising:
  • a supercritical or near critical water generator described herein;
  • a fuel handling system adapted to transport said fuel composition to said fuel combustion apparatus;
  • a water circulation system adapted to transport said compressed water in proximity of said fuel combustion apparatus adequate to heat said compressed water to a temperature of at least about 373° C. to produce said supercritical or near critical water; and
  • optional controls.
  • In certain embodiments, the fuel combustion apparatus adapted for combusting a fuel composition comprising lignin having a heating value of at least about 5,000 BTU/lb, preferably, at least about 7,500 BTU/lb, and even more preferably about 8,000 BTU/lb to about 12,000 BTU/lb, wherein the heating value is measured by ASTM-D240 or D5865.
  • In certain embodiments, the fuel handling system is adapted to transport said fuel comprising lignin, wherein said lignin is in a powdered form, including both wet and dry powders. In certain embodiments, the fuel handling system is adapted to transport said fuel comprising lignin, wherein said lignin is in a pelletized form, including both wet and dry pellets. In certain embodiments, the fuel handling system is adapted to transport said fuel composition comprising lignin, wherein said lignin is in a liquid form. In certain other embodiments, the fuel handling system is adapted to transport said fuel composition comprising lignin, wherein said lignin is a combination of powdered form, pelletized form, and/or liquid form.
  • In certain embodiments, the system further comprises at least one preheater for said water or said compressed water in association with said water circulation system. In certain preferred embodiments, the preheater heats said water or said compressed water to a temperature of about 100° C. and about 300° C.
  • The present invention is further defined in the following Examples, in which all parts and percentages are by weight, unless otherwise stated. It should be understood that these examples, while indicating preferred embodiments of the invention, are given by way of illustration only and are not to be construed as limiting in any manner. From the above discussion and these examples, one skilled in the art can ascertain the essential characteristics of this invention, and without departing from the spirit and scope thereof, can make various changes and modifications of the invention to adapt it to various usages and conditions.
  • EXAMPLES SCW Requirements
  • A lignin-fired SCW generator useful in the methods and systems may be used at the commercial scale at a feed rate of about 1000 dry tons/day of biomass. Based on modeling, the heat requirement equals approximately 200 MMBTU/hr. A suitable range of conditions for the lignin-fired SCW generator of the invention is shown in Table 1.
  • TABLE 1
    Design Element Minimum Maximum Comment
    Hours of Operation 8,000 8,424 50 weeks/year, 24 hours/7 days
    Temperature 450° C. (797° F.) 550° C. (887° F.) SCW temperature at outlet
    Pressure 221 bar 300 bar SCW pressure at outlet
    Flow 300,000 lb/hr 400,000 lb/hr SCW mass flow rate
    Water pre-heat 150° C. 250° C. Water temperature at inlet of the SCW generator, pre-
    temperature heated through a recovery heat exchanger
    Heat Duty 200 MMBTU/hr 300 MMBTU/hr
    Turn Down 75% 100%  Operating capacity
    Primary Fuel Process derived lignin
    Moisture Content
    25% 35% Air dried under cover in piles
    Particle Size 60 mesh 10 mesh
    Secondary/Backup Fuel Natural gas, expected use for 10% operating time
    Combustion Air
    15% 50% Excess air, no preconditioning
    Water Supply
    BOD5
    2 mg/L
    Cl 0.1 mg/L Residual chlorine
    Hardness 40 mg/L As CaCO3
    Burner Typical circular, center feed port, with annular
    air/secondary fuel feeds
    Combustion Chamber Ceramic refractory with soot blowing capabilities
    (Firebox)
    Heat Transfer Section ½″-2″ serpentine coils of 316L, with soot blowing
    capabilities
    Flue Gas 280° C. 325° C. Add on NOx and PM controls
    Ash Handling Conventional equipment and design
    Construction/Modularity 2 coils per generator
  • Other Embodiments Process Conditions
  • In certain preferred embodiments, the SCW generator needs to be capable of producing sub-critical and supercritical water at the conditions shown in Table 1 above.
  • The generator should utilize as its primary fuel the process-derived lignin with natural gas as secondary/backup. The generator should also be capable of about 25% turn down, i.e., from 100% to 75% operating capacity.
  • Primary Fuel Basis
  • The process derived lignin exits the process at a moisture content (MC) between about 50% and about 60%. Lignin above 35% MC may be difficult to combust, so some form of drying is preferred. The simplest method of drying is taking the lignin from the process separator and air dry it in a covered pile that is turned frequently for several days. Alternatively, excess process heat may be used to facilitate drying and shorten the drying cycle time. The high heating value, % volatile material, ash content, and ash fusion temperature are all important characteristics to monitor.
  • The lignin, upon drying, agglomerates to a particle size of approximately 60 mesh. The material is easily crumbled further, so no additional size reduction is anticipated. If a secondary biomass fuel, such as bark, is to be utilized, it is size reduced to the approximate lignin size and well mixed prior to combustion.
  • Combustion Air
  • For the most efficient combustion of the lignin at about 35% MC, the burner is capable of handling 50% excess air. This parameter may drop to about 15% if the lignin moisture content also dropped to about 15% to about 20%. The air is not expected to require any preheating or conditioning. The combustion air is blown in with the lignin through the burner. Excess air is supplied as either under fired, over fired, or a combination of under and over fired, again with blowers. The generator preferably has the capability of supplying both. In addition to ambient air as the oxidant, pure oxygen (O2) would also work, but is not preferred due to cost.
  • SCW Supply
  • It is important to know the characteristics of the water supplied to the generator. Because of the extreme conditions in the generator, there should be minimal concentrations of chlorine and biological oxygen demand (BOD), and low/minimal concentrations of hardness and dissolved solids. Depending upon the source, pretreatment may include carbon filtration, softening, and membrane separation through a reverse osmosis (RO) unit.
  • The SCW feed may be pumped to pressure (about 4,100 psi (283 bar)) then optionally preheated (by a process heat recovery exchanger) to about 392° F. (200° C.) just prior to entering the generator.
  • Burner
  • The burner 34 may be of typical design with a center feed port 35 for solid fuel surrounded by concentric forced air ports 36 and secondary fuel ports 37, such as shown in FIG. 2:
    • 34 Burner
    • 35 Center feed port
    • 36 Forced air port
    • 37 Secondary fuel port
      In some embodiments, the burner 24 may generate a flame length of approximately 30 feet horizontally and is dependent upon fuel particle size, moisture and carbon content. The flame temperature is between about 1,800° F. (982° C.) and about 2,000° F. (1,093° C.).
  • The solid fuel port may be at least about 4″ in diameter, preferably about 6″ to about 8″ and about 4′ to about 6′ long, made of carbon steel, with enough flow to push flame temperature away from the burner end. The ports may be swirled to discharge fuel in a helical pattern within the firebox for increased travel length and burn time allowing for more complete combustion. Flame temperature preferably do not decrease significantly with turn down
  • Combustion Chamber (Firebox) of Generator
  • The size of the chamber may be about 40′ long and combined with the heat transfer section be about 30′ high. Ceramic refractory may be used for lining the chamber. As with any solid fuel, soot collecting on the outside of the tubes and within the firebox is a consideration. Allowance is made for pressure washing and/or the installation of soot blowers to minimize this fouling.
  • Heat Transfer Section of Generator
  • The process coil may be positioned above the burner firebox in a position to allow cross flow of the heated flue gas. In certain embodiments, it may be serpentine with 180° bends and seamlessly finned to enhance convective heat transfer. The coil may include about 1″ to about 2″ outside diameter tubes of stainless steel. Stainless steel (SAE 316L) is a suitable material of construction; however, because of the high pressure and possible sulfur impacts from the lignin, the material of construction may preferably include Inconel.
  • Flue Gas
  • In certain embodiments, it is desirable to add air pollution control devices for the nitrogen oxides (NOx) and particulate matter (PM) emitted. The flue gas should be no cooler than about 550° F. (288° C.) to avoid acid gas dew point issues and the accompanying corrosion concerns for the exhaust ducts and stack. Higher temperatures would allow for a smaller coil.
  • Because of the heat duty of the generator, NOx and PM need to be controlled to certain emission rate limits. High temperature baghouses or electrostatic precipitators (ESPs) are suitable for controlling PM. Selective catalytic or selective non-catalytic reduction (SCR/SNCR) units are suitable for controlling NOx as long as ammonia slip is adequately addressed.
  • Ash Handling
  • A rotary valve with drag chain conveyor (or equivalent) may be incorporated for ash handling.
  • Supercritical Water (SCW) or Near-Critical Water (NCW)
  • Once the water has been heated to supercritical or near critical conditions in the generator, it is injected directly into the process stream. In certain embodiments, the SCW or NCW is utilized as a “once through” utility. In other embodiments, the SCW or NCW may be recovered, treated, and reused.
  • Construction/Modularity
  • In certain embodiments of the SCW or NCW generator, it is of a transportable scale with two complete coil assemblies per generator. Splitting into two assemblies also minimizes the field erection and welding concerns allowing much of the welding to be performed at the shop versus in the field.
  • Startup/Shutdown
  • The SCW or NCW generator may be cold/warm started with water. Either natural gas or lignin may be used as the startup fuel with the possibility of using other biomass fuels if sized appropriately. Heat up of the unit is preferably slow and steady to avoid building up heat stresses at the entrances to the generator, the locations where the greatest temperature differentials exist.
  • For shutdowns, it is preferred that the generator never goes cold, but maintains a certain (warm) temperature in the firebox. Cold restarts create large heat stresses that can damage the generator.
  • Using the lignin as a fuel minimizes process operating costs and optimizes the overall process two-fold: it removes a large solid waste stream that would otherwise have to be disposed of and it minimizes the amount of fossil fuels combusted thus minimizing greenhouse gas emissions.
  • When ranges are used herein for physical properties, such as molecular weight, or chemical properties, such as chemical formulae, all combinations, and subcombinations of ranges specific embodiments therein are intended to be included.
  • The disclosures of each patent, patent application, and publication cited or described in this document are hereby incorporated herein by reference, in their entirety.
  • Those skilled in the art will appreciate that numerous changes and modifications can be made to the preferred embodiments of the invention and that such changes and modifications can be made without departing from the spirit of the invention. It is, therefore, intended that the appended claims cover all such equivalent variations as fall within the true spirit and scope of the invention.

Claims (21)

1. (canceled)
2. A method of generating supercritical or near critical water, comprising:
providing water;
heating said water to a temperature of at least about 373° C. to form superheated steam;
applying to said superheated steam a pressure of at least about 221 bar;
wherein said heating comprises combusting a fuel composition comprising lignin; and
wherein said lignin has a heating value of at least about 3,000 BTU/lb.
3. The method of claim 2,
wherein said lignin has a heating value of at least about 5,000 BTU/lb.
4. The method of claim 2,
wherein said lignin has heating value of at least about 7,500 BTU/lb.
5. The method of claim 2,
wherein said lignin is in a powdered form.
6. The method of claim 2,
wherein said lignin is in a pelletized form.
7. The method of claim 2,
wherein said lignin is in a liquid form.
8. The method of claim 2,
wherein said lignin is produced from a material comprising lignocellulose.
9. The method of claim 2,
wherein said fuel composition further comprises at least one supplemental fuel.
10. The method of claim 9,
wherein said supplemental fuel is selected from the group consisting of biomass, natural gas, coal, and mixtures thereof.
11. The method of claim 2,
wherein said water in said providing step is at about ambient pressure and about ambient temperature.
12. The method of claim 2,
wherein said water in said providing step is clean water.
13. The method of claim 2, further comprising:
preheating said water prior to said step of heating.
14. The method of claim 13,
wherein said water is preheated to a temperature of about 100° C. to about 300° C.
15. The method of claim 2,
wherein said step of heating is carried out as multiple steps.
16. The method of claim 2,
wherein said step of applying is carried out as multiple steps.
17. (canceled)
18. The method of claim 2,
wherein said method is a continuous process.
19. The method of claim 2,
wherein said method is a batch or semi-batch process.
20. The method of claim 2, further comprising:
drying said fuel composition comprising lignin.
21-30. (canceled)
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10253057B2 (en) 2014-11-12 2019-04-09 Renmatix, Inc. Method of coalescing a substance
EP3502118A1 (en) 2017-12-22 2019-06-26 Universidad De Valladolid Ultra-fast lignin depolymerization process

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8546560B2 (en) * 2008-07-16 2013-10-01 Renmatix, Inc. Solvo-thermal hydrolysis of cellulose
CA2730766C (en) * 2008-07-16 2016-11-01 Sriya Innovations, Inc. Method of extraction of furfural and glucose from biomass using one or more supercritical fluids
CA2945277C (en) 2010-01-19 2021-01-05 Renmatix, Inc. Production of fermentable sugars and lignin from biomass using supercritical fluids
US8801859B2 (en) 2011-05-04 2014-08-12 Renmatix, Inc. Self-cleaning apparatus and method for thick slurry pressure control
SG194724A1 (en) 2011-05-04 2013-12-30 Renmatix Inc Lignin production from lignocellulosic biomass
CA2844420A1 (en) 2011-08-31 2013-03-07 Iogen Energy Corporation Process for recovering salt during a lignocellulosic conversion process
US8759498B2 (en) * 2011-12-30 2014-06-24 Renmatix, Inc. Compositions comprising lignin
BR112015000582A2 (en) * 2012-07-13 2017-06-27 Renmatix Inc method, and composition
CN105189616A (en) 2013-03-15 2015-12-23 瑞恩麦特克斯股份有限公司 High purity lignin, lignin compositions, and higher structured lignin
US9255187B2 (en) * 2013-03-15 2016-02-09 Synergy Horizon Limited Method for production of dry hydrolytic lignin
BR112017005997B1 (en) 2014-09-26 2021-10-05 Renmatix, Inc METHOD FOR MANUFACTURING COMPOSITIONS THAT CONTAIN CELLULOSE
GR1010526B (en) * 2022-10-12 2023-08-10 Δενεσακης, Ιωαννης Αναστασιου Method and system (mechanism) integrated into the production process of the technology used in the conversion of solid biomass into, inter alia, solid biofuel pellets and briquettes

Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2822784A (en) * 1955-05-09 1958-02-11 Babcock & Wilcox Co Apparatus for and method of generating and superheating vapor
US4535593A (en) * 1981-08-28 1985-08-20 Hitachi, Ltd. Method of and apparatus for warming high-pressure feed water heaters for power plants
US4674285A (en) * 1983-05-16 1987-06-23 The Babcock & Wilcox Company Start-up control system and vessel for LMFBR
US5558783A (en) * 1993-02-05 1996-09-24 Mcguinness; Thomas G. Supercritical oxidation reactor
US20010050096A1 (en) * 2000-04-18 2001-12-13 Costantini Michael A. Supercritical fluid delivery and recovery system for semiconductor wafer processing
US20070217980A1 (en) * 2004-10-22 2007-09-20 Asdrubal Garcia-Ortiz Systems and Methods for Water Purification Using Supercritical Water Oxidation
US20090169418A1 (en) * 2006-02-05 2009-07-02 Sandvik Intellectual Property Ab Component for supercritical water oxidation plants, made of an austenitic stainless steel alloy
US20090205546A1 (en) * 2008-02-15 2009-08-20 Renewable Densified Fuels, Llc Densified fuel pellets
US20090223612A1 (en) * 2007-11-16 2009-09-10 Mcknight James K Powdered fuels and powdered fuel dispersions
US20100055629A1 (en) * 2006-11-17 2010-03-04 Summerhill Biomass Systems, Inc. Powdered fuels, dispersions thereof, and combustion devices related thereto
US20100200229A1 (en) * 2009-02-10 2010-08-12 HAMCO Energy Corporation System and method for hydrocarbon recovery and extraction
US20110171709A1 (en) * 2007-11-01 2011-07-14 Mascoma Corporation Product Recovery From Fermentation of Lignocellulosic Biomass
US20110237838A1 (en) * 2005-05-02 2011-09-29 University Of Utah Research Foundation Processes for catalytic conversion of lignin to liquid bio-fuels and novel bio-fuels
US20110239973A1 (en) * 2008-11-03 2011-10-06 Caidong Qin Fuel mixture containing combustible solid powder and engine using the fuel mixture

Family Cites Families (29)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4714591A (en) * 1983-12-22 1987-12-22 Domtar Inc. Apparatus and method involving supercritical fluid extraction
US4987954A (en) * 1988-11-28 1991-01-29 Boucher Robert J Fuel reactor
US5429645A (en) * 1990-12-06 1995-07-04 Benson; Peter H. Solid fuel and process for combustion of the solid fuel
US5705369A (en) 1994-12-27 1998-01-06 Midwest Research Institute Prehydrolysis of lignocellulose
US6022419A (en) 1996-09-30 2000-02-08 Midwest Research Institute Hydrolysis and fractionation of lignocellulosic biomass
US6228177B1 (en) 1996-09-30 2001-05-08 Midwest Research Institute Aqueous fractionation of biomass based on novel carbohydrate hydrolysis kinetics
JP2001050010A (en) 1999-08-10 2001-02-23 Toshiba Corp Power plant
JP2001079571A (en) 1999-09-14 2001-03-27 Toshiba Corp Supercritical water oxidation reaction process, supercritical water reaction plant and utility plant
JP4683748B2 (en) 2001-03-07 2011-05-18 ヤンマー株式会社 Reactor reaction equipment with supercritical water or subcritical water
DE10162202B4 (en) 2001-12-18 2007-12-27 Fraunhofer-Gesellschaft zur Förderung der angewandten Forschung e.V. Hydrocarbon reformer
CN101449001B (en) 2006-03-29 2013-05-08 弗吉尼亚暨州立大学知识产权公司 Fractionation of cellulose-solvent-borne type lignocellulose with a moderate reaction condition and a reagent circulation
WO2008076947A2 (en) 2006-12-16 2008-06-26 Papile Christopher J Methods and/or systems for removing carbon dioxide and/or generating power
CN103819688B (en) 2008-03-14 2017-04-12 弗吉尼亚暨州立大学知识产权公司 Method and apparatus for lignocellulose pretreatment by using super-cellulose-solvent and highly volatile solvents
GB0812669D0 (en) 2008-07-11 2008-08-20 Kinney John Method and apparatus for generating power from biomass
US8282738B2 (en) 2008-07-16 2012-10-09 Renmatix, Inc. Solvo-thermal fractionation of biomass
CA2730766C (en) 2008-07-16 2016-11-01 Sriya Innovations, Inc. Method of extraction of furfural and glucose from biomass using one or more supercritical fluids
BRPI0919771A2 (en) 2008-10-17 2015-08-18 Mascoma Corp Pure lignin production from cellulosic ligno biomass
UA103064C2 (en) * 2008-11-24 2013-09-10 Рве Пауер Акциенгезелльшафт Method for formation of engineering steam
US20110126448A1 (en) 2008-12-17 2011-06-02 BP Biofuels UK Limited Process, Plant, and Biofuel For Integrated Biofuel Production
US20110076724A1 (en) 2008-12-17 2011-03-31 BP Biofuels UK Limited Process, Plant, and Biofuel for Integrated Biofuel Production
US8152867B2 (en) 2008-12-17 2012-04-10 Bp Biofuels Uk Ltd. Process, plant and biofuel for integrated biofuel production
US20100146842A1 (en) 2008-12-17 2010-06-17 Bp Corporation North America Inc. Process, plant and biofuel for integrated biofuel production
IT1393929B1 (en) 2008-12-18 2012-05-17 Eni Spa PROCEDURE FOR THE PRODUCTION OF BIO-OIL FROM BIOMASS
CN102575422B (en) 2009-07-13 2016-08-03 贝塔可再生资源公司 The separating at high temperature method of lignin
KR101130722B1 (en) 2009-10-30 2012-03-28 한국전력공사 Steam producing apparatus using supercritical water oxidation apparatus
US20110108491A1 (en) * 2009-11-10 2011-05-12 Palo Alto Research Center Incorporated Desalination using supercritical water and spiral separation
JP5568433B2 (en) * 2010-10-14 2014-08-06 東京エレクトロン株式会社 Water treatment apparatus and water treatment method
US9187335B2 (en) * 2011-03-30 2015-11-17 Altmerge, Llc Pulse jet water desalination and purification
US8721980B2 (en) * 2011-03-30 2014-05-13 Altmerge, Llc Systems and methods of producing chemical compounds

Patent Citations (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2822784A (en) * 1955-05-09 1958-02-11 Babcock & Wilcox Co Apparatus for and method of generating and superheating vapor
US4535593A (en) * 1981-08-28 1985-08-20 Hitachi, Ltd. Method of and apparatus for warming high-pressure feed water heaters for power plants
US4674285A (en) * 1983-05-16 1987-06-23 The Babcock & Wilcox Company Start-up control system and vessel for LMFBR
US5558783A (en) * 1993-02-05 1996-09-24 Mcguinness; Thomas G. Supercritical oxidation reactor
US20010050096A1 (en) * 2000-04-18 2001-12-13 Costantini Michael A. Supercritical fluid delivery and recovery system for semiconductor wafer processing
US20070217980A1 (en) * 2004-10-22 2007-09-20 Asdrubal Garcia-Ortiz Systems and Methods for Water Purification Using Supercritical Water Oxidation
US20110237838A1 (en) * 2005-05-02 2011-09-29 University Of Utah Research Foundation Processes for catalytic conversion of lignin to liquid bio-fuels and novel bio-fuels
US20090169418A1 (en) * 2006-02-05 2009-07-02 Sandvik Intellectual Property Ab Component for supercritical water oxidation plants, made of an austenitic stainless steel alloy
US20100055629A1 (en) * 2006-11-17 2010-03-04 Summerhill Biomass Systems, Inc. Powdered fuels, dispersions thereof, and combustion devices related thereto
US20110171709A1 (en) * 2007-11-01 2011-07-14 Mascoma Corporation Product Recovery From Fermentation of Lignocellulosic Biomass
US20090223612A1 (en) * 2007-11-16 2009-09-10 Mcknight James K Powdered fuels and powdered fuel dispersions
US7960325B2 (en) * 2008-02-15 2011-06-14 Renewable Densified Fuels, Llc Densified fuel pellets
US20090205546A1 (en) * 2008-02-15 2009-08-20 Renewable Densified Fuels, Llc Densified fuel pellets
US20110239973A1 (en) * 2008-11-03 2011-10-06 Caidong Qin Fuel mixture containing combustible solid powder and engine using the fuel mixture
US20100200229A1 (en) * 2009-02-10 2010-08-12 HAMCO Energy Corporation System and method for hydrocarbon recovery and extraction

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10253057B2 (en) 2014-11-12 2019-04-09 Renmatix, Inc. Method of coalescing a substance
US10633405B2 (en) 2014-11-12 2020-04-28 Renmatix, Inc. Method of coalescing a substance
EP3502118A1 (en) 2017-12-22 2019-06-26 Universidad De Valladolid Ultra-fast lignin depolymerization process
WO2019120956A1 (en) 2017-12-22 2019-06-27 Universidad De Valladolid Ultra-fast lignin depolymerization process

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