WO2009127727A1 - Process for converting biomass to coal-like material using hydrothermal carbonisation - Google Patents

Process for converting biomass to coal-like material using hydrothermal carbonisation Download PDF

Info

Publication number
WO2009127727A1
WO2009127727A1 PCT/EP2009/054602 EP2009054602W WO2009127727A1 WO 2009127727 A1 WO2009127727 A1 WO 2009127727A1 EP 2009054602 W EP2009054602 W EP 2009054602W WO 2009127727 A1 WO2009127727 A1 WO 2009127727A1
Authority
WO
WIPO (PCT)
Prior art keywords
biomass
coal
reaction mixture
liquid phase
temperature
Prior art date
Application number
PCT/EP2009/054602
Other languages
English (en)
French (fr)
Inventor
Markus Antonietti
Original Assignee
Csl Carbon Solutions Ltd.
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Csl Carbon Solutions Ltd. filed Critical Csl Carbon Solutions Ltd.
Priority to US12/988,193 priority Critical patent/US20110056125A1/en
Priority to BRPI0911421A priority patent/BRPI0911421A2/pt
Priority to CA2737596A priority patent/CA2737596A1/en
Priority to EP09733412A priority patent/EP2274405A1/en
Priority to AU2009237607A priority patent/AU2009237607A1/en
Publication of WO2009127727A1 publication Critical patent/WO2009127727A1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/44Solid fuels essentially based on materials of non-mineral origin on vegetable substances
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/02Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L9/00Treating solid fuels to improve their combustion
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/02Treating solid fuels to improve their combustion by chemical means
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/08Treating solid fuels to improve their combustion by heat treatments, e.g. calcining
    • C10L9/086Hydrothermal carbonization
    • 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
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • 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
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/145Feedstock the feedstock being materials of biological origin

Definitions

  • the present invention relates generally to a process for the preparation of coal-like material from biomass, more particularly to an improved and quicker process yielding the coal-like material in enhanced space-time yield, and which, moreover, allows for enhanced quality control of the final product, as well as improved reproducibility. Also, the process of the invention is cheaper in terms of the necessary equipment, and it is a very safe process.
  • the optimum reaction conditions involve a heating of a biomass dispersion under weakly acidic conditions in a closed reaction vessel for 4 - 24 h to temperatures of around 200 0 C.
  • the HTC of biomass to afford carbon-like products was carried out as a one-step process.
  • US 2008/0006518 Al relates to a process for reforming a biomass by heating the biomass in pressurized hot water to carbonize the biomass.
  • the process comprises performing a primary heating of the biomass gradually at a temperature ranging from 200 to 260 0 C, and then performing a secondary heating of the biomass at a temperature ranging from 270 to 330 0 C.
  • the products of the process are referred to as carbides.
  • the obtained carbides contain approximately 75 wt% of carbon. Owing to the temperatures close to the critical range which are used in the U.S. patent application, the process is complex and requires elaborate and thus expensive equipment to be carried out with safety.
  • Fig. 1 provides a schematic flow diagram showing a preferred mode of carrying out the process of the invention in a continuous mode.
  • the process for the preparation of coal-like material according to the present invention can be referred to as a hydrothermal process, in particular as a hydrothermal carbonisation process.
  • This terminology is intended to show that the process involves the heating of a reaction mixture comprising water and will yield carbonized coal-like material .
  • biomass as used herein is broadly understood as encompassing all kinds of plant and animal material and material derived from the same. According to a preferred embodiment, biomass as meant in the present specification shall not include petroleum or petroleum derived products.
  • the biomass for use in the present invention may comprise macromolecular compounds, examples of which are lignin and polysaccharides, such as starch, cellulose, and glycogen.
  • lignin and polysaccharides such as starch, cellulose, and glycogen.
  • cellulose is intended to encompass hemicelluloses commonly also referred to as polyoses .
  • biomass may include both, plant and animal-derived material.
  • manure dung
  • night soil sewage sludge
  • the biomass for use in the present invention is preferably plant biomass, i.e. biomass of or derived from plants
  • certain contents of animal biomass i.e. biomass of or derived from animals
  • the biomass may contain up to 30 % of animal biomass .
  • the biomass for use in the present invention which is preferably plant biomass, contains more than 70 wt%, most preferably > 90 wt%, of polysaccharides and lignines in terms of the solid contents of the biomass .
  • the plant biomass may be agricultural plant material (e.g. agricultural wastes) or all kinds of wood material .
  • biomass examples include crop, agricultural food and waste, feed crop residues, wood (such as wood flour, wood waste, scrap wood, sawdust, chips and discards) , straw (including rice straw) , grass, leaves, chaff, and bagasse.
  • wood such as wood flour, wood waste, scrap wood, sawdust, chips and discards
  • straw including rice straw
  • grass leaves, chaff, and bagasse.
  • industrial and municipal wastes, including waste paper can be exemplified.
  • biomass as used herein preferably also includes monosaccharides such as glucose, ribose, xylose, arabinose, mannose, galactose, fructose, sorbose, fucose and rhamnose, as well as oligosaccharides.
  • coal-like material refers to a material, which is similar to natural coal in terms of property and texture. Owing to the method of the preparation thereof, it may also be referred to as hydrothermal coal. It is a product, more precisely a carbonized product that is obtained or obtainable by the hydrothermal carbonization process of the invention .
  • the coal-like material can be distinguished from synthetic resins, including those synthetic resins, which have been prepared using monomers obtained from lignocellulosic material, such as phenolic resins, and in particular novolac-type phenolic resins.
  • synthetic resins are preferably not encompassed by the expression "coal-like material" as used herein.
  • the coal-like material obtained in the process of the present invention typically comprises, without limitation, ⁇ 70 wt% of carbon, for example 60 to 65 wt% of carbon.
  • the coal-like material obtained in the process of the invention can have a carbon content of > 50 wt% of carbon, which is significantly above the carbon content of dried (raw) biomass, which is in the order of 40 wt% .
  • the coal-like material of the invention may comprise 65 to 72 wt% of carbon.
  • the above carbon contents refer to the dry mass of the coal-like materials.
  • the carbon content of the coal-like materials can be determined by elemental analysis (combustion) .
  • the carbon content of the materials can be measured using a Vario
  • coal-like material as meant herein is more aliphatic than e.g. the product presumably obtained in US 2008/0006518, which is more aromatic.
  • the coal- like material obtained in the hydrothermal carbonisation process of the present invention has a high calorific value, for instance > 23 MJ/kg, preferably 24 to 38 MJ/kg, and more preferably 24 to 32 MJ/kg.
  • the calorific value of the coal-like material can be determined by standard calorimetry. More specifically, in the present invention, the calorific values of the materials can be determined in accordance with DIN 51900 or BGS RAL-GZ 724. As will be appreciated, the above calorific values of the coal -like material are expressed in terms of the dry mass of the coal-like material (in kg ⁇ .
  • the carbon content and the calorific value of the coal-like material are indicative of the high degree of carbonization of the coal-like material of the invention that can be achieved in the process of the present invention.
  • the coal- like material of the invention that is obtained by polymerization of the activated biomass initiated by the addition of a polymerization initiator in step (ii), has a carbon content of > 50 wt% (in terms of the dry mass of the coal-like material) and a calorific value of > 23 MJ/kg (in terms of the dry mass of the coal- like material ⁇ .
  • the "dry mass" of the coal-like material refers to the mass thereof after drying under such drying conditions that no further loss of water is observed.
  • the dry mass can refer to the mass of the coal-like material after drying at a temperature of 80 0 C for at least 24 h.
  • step (i) i.e. the first step
  • the biomass is activated for the subsequent polymerization to coal-like material in the second step.
  • the mechanism of the activation in step (i) is assumed to be as follows.
  • the macromolecular species e.g. the polysaccharides contained in or constituting the biomass may be molten or dissolved in water.
  • cellulose contained in the biomass which is a crystalline material, will be molten in water.
  • the polysaccharides can be disintegrated or broken down to smaller fragments, such as monosaccharides and oligosaccharides . Those fragments will undergo consecutive rapid dehydration to more reactive intermediates, which are capable of undergoing rapid conversion to coal-like material, i.e. coalification, in the second step.
  • the reactive intermediates can also be referred to as "coal monomers".
  • the dehydration of glucose to hydroxymethyl furfural is an example for such a dehydration reaction.
  • These "coal monomers 11 are typically characterized by increased chemical reactivity towards intermolecular reactions, as compared to the raw biomass, e.gr. via vinylic subunits, reactive aldehyde side groups, or activated hydroxymethyl groups onto furane moieties.
  • the first step of the hydrothermal carbonization process of the invention can also be referred to as the activation step, and the intermediate product of that step as activated biomass.
  • the water being present in the reaction mixture of the first step may be water adhering or bound to the original biomass, which can also be referred to as "raw” biomass.
  • the biomass to be subjected to step (i) is also referred to as raw biomass.
  • raw biomass may for instance be the biomass obtained as waste (e.g. wood, agricultural, municipal waste) from the provider, without further treatment, or as collected from natural sources.
  • the raw wood biomass may be the wood collected in the forest (as the natural source) , or sawdust from the wood processing industry.
  • the water content of raw biomass may for instance be up to 80 wt% .
  • the raw biomass can be used as such and with water contents as mentioned above.
  • the ⁇ raw ⁇ biomass to be subjected to the process of the invention is preferably not dried. Consequently, the present invention allows avoiding the energy-consuming drying of the biomass.
  • water may be added to the wet or dry biomass to adjust the water content in the reaction mixture of step (i) .
  • the total amount of water, i.e. the water bound to or contained in the as-obtained biomass and the additional water is not specifically limited.
  • the weight ratio of water to biomass (water/biomass) in the reaction mixture of the first step is in the range of 0.3 to 10.
  • the solid contents of the reaction mixture to be subjected to the step (i) is preferably 5 to 35%, more preferably 10 to 30%, especially 15 to 25% by weight.
  • the reaction mixture having such solid contents is preferably in the form of a slurry.
  • the reaction mixture comprising water and biomass to be subjected to heating in the first step may comprise, without limitation, further ingredients as long as these will not inhibit the activation of the biomass.
  • the hydrothermal carbonisation process of the present invention can be carried out in water alone.
  • Organic solvents such as ketones are unnecessary, and they are preferably omitted.
  • the reaction mixture of step (i) contains water as a single solvent, with other solvents such as ethanol only incidentially brought in by the biomass, e.g. by fermentation. Consequently, preferably at least 95 wt%, more preferably at least 98 wt% of the solvent present in the reaction mixture of the first step is water.
  • the pH is preferably in the range of 3 to 7, more preferably 4 to 6.
  • the disintegration, in particular of polymeric compounds in the biomass, e.g. by hydrolysis can be accelerated, and the yield of activated biomass, e.g. smaller fragments can be increased.
  • biomass which are more difficult to activate than others.
  • Wood is an example of biomass, which is quite difficult to activate.
  • the pH is adjusted to lie within the acidic range with particular benefit.
  • the desired pH of the reaction mixture in the first step can be controlled to lie within the above ranges by adding suitable acids, which do not interfere with the activation of the biomass.
  • the acid is preferably a strong acid, e.g. having a pK a of less than 4.5, Both, anorganic acids, e.g. mineral acids, and organic acids can be used.
  • An example of a suitable mineral acid is phosphoric acid.
  • Citric acid, lactic acid and pyruvic acid are examples of (strong) organic acids.
  • an acid such as those exemplified above is added to the reaction mixture prior to or during step (i) for the adjustment of the pH of the reaction mixture to lie in the range of 3 to I 1 especially 4 to 6.
  • the reaction mixture to be subjected to the step (i) which may e.g. comprise an acid in addition to the (raw) biomass and water, can be prepared in a suitable mixer.
  • step (i) Dependent on which type of biomass is used as a starting material, the particular reaction conditions in step (i) may be selected appropriately.
  • the duration of the activation step may be shorter and the pH less acidic than for polymeric biomass starting material.
  • the heating temperature (or the reaction temperature) in step (i) is not particularly limited, as long as it is sufficient to convert at least larger parts of the (raw) biomass subjected to the process to activated biomass as defined herein.
  • the heating temperature is such that at least 80 wt% of the raw biomass are converted to activated biomass.
  • the heating temperature (or the reaction temperature) may be in the range of 190 to 270 0 C, and it preferably is 210 to 250 0 C, more preferably 230 to 240 0 C.
  • the reaction temperature in step (i) is occasionally denoted T ⁇ .
  • the temperature is 210 to 250 0 C
  • the pH value is acidic, especially 3 to 7.
  • the reaction time of step (i) (i.e. until at least 80 wt% of the biomass have been converted to activated biomass as meant herein) can be reduced to 5 to 15 minutes, preferably 5 to 10 minutes.
  • the duration of the first step will depend on the kind of biomass used.
  • the (raw) biomass to be subjected to the first step may be used in any form. Preferably, however it is divided into an appropriate particle size prior to use, e.g. in the range of 0.1 to 20 mm, more preferably 0.3 to 10 mm, especially 0.5 to 5 mm. Suitable particle sizes such as those exemplified above can be obtained by methods such as grinding, chopping or sawing.
  • the activated biomass present in the reaction mixture obtained in step (i) comprises the products of the disintegration and/or dehydration of the starting "raw” biomass as detailed above, collectively referred to as “activated biomass” in the present specification.
  • step (ii) the activated biomass is subjected to polymerization to give coal-like material as defined above.
  • the "activated biomass” obtained in step (i) will be polymerized in step (ii)
  • the "activated biomass” may in the alternative be referred to as "polymerizable biomass”.
  • the polymerization in the second step is initiated by- addition a polymerization initiator to the reaction mixture.
  • the "polymerization” which takes place in the second step (i.e. in step (ii) ⁇ is to be construed broadly and means any reaction of molecules of the activated biomass resulting in the built-up of larger molecules eventually yielding coal-like material.
  • the polymerization may include chain-growth of the monomers and inter-chain cro ⁇ slinking .
  • the polymerization will yield coal-like material, which preferably has, in terms of the dry mass thereof, a carbon content of > 50 wt% and a calorific value of > 23 MJ/kg.
  • the polymerization initiator is added in step ⁇ ii) as a reactant to initiate the polymerization resulting in coal-like material, which preferably has a carbon content and calorific value as indicated above.
  • the reaction mixture obtained in step (i) is directly subjected to step ⁇ ii) , i.e. without any intermediate treatment.
  • the reaction mixture obtained in step (i) may be cooled by allowing to stand or by active cooling, prior to adding the polymerization initiator to start step (ii ⁇ .
  • step (i) it may be noted that some polymerization of components contained in the activated biomass may take place already in step (i) .
  • the polymerization step (ii) as such is initiated by adding the polymerization initiator.
  • the polymerization initiator for use in the present invention is not specifically limited in kind, as long as it is suitable to initiate the polymerization of the activated biomass to the carbon-like material in the second step of the hydrothermal carbonization process of the present invention.
  • the polymerization initiator is usually capable of generating radicals which will start the polymerization of the activated biomass to coal-like material.
  • Useful polymerization initiators are for instance azo compounds, peroxides, oxygen and redox initiators, as well as mixtures thereof .
  • the azo compound may be azobisisobutyronitrile.
  • Useful peroxides are inorganic peroxides, e.g.
  • persulfates such as potassium persulfate and ammonium persulfate
  • metal peroxides such as (C2H5 ⁇ 2BOOC2H5 and compounds obtained by replacing the boron atom of (C2H5) 2BOOC2H5 with Al or Zn
  • organic peroxides e.g., acyl peroxides such as benzoyl peroxide, alkyl peroxides such as t-butyl peroxide and cumyl peroxide, peroxy acid esters such as t-butyl peroxalate, or hydrogen peroxide.
  • the redox initiator there may be used hydrogen peroxide-Fe ⁇ + (Fenton 1 s reagent) , persulfate and sulfite and cumene hydroperoxide-amine-based compounds.
  • copper salts such as CuCl2 can be used.
  • FeCl3 and H2O2 are used as the redox initiator.
  • polymerization initiators known to be useful for the hardening of unsaturated polyesters are also useful to initiate the polymerization in the second step of the present process.
  • Warm hardeners are typically peroxides which will be decomposed at their decomposition temperature to form a radical which will start the polymerization, i.e. carbonization, to yield the target coal-like material.
  • peroxides are benzoyl peroxide, cumolhydroperoxide, methy1isobutyIketonperoxide, and tert.- butylperoxybenzoate.
  • the reaction mixture in the second step is preferably heated to or above the decomposition temperature of the peroxide to generate radicals, when warm hardeners are used as polymerization initiators .
  • the second type of polymerization initiators which are likewise useful in the process of the present invention are often referred to as cold hardeners, e.g. in the field of unsaturated polyesters.
  • Cold hardeners representing suitable polymerization initiators for use in the present invention generally comprise an accelerator compound and a peroxide, the peroxide being added with preference after the accelerator compound.
  • the accelerator compound are iron salts.
  • Suitable peroxides are e.g. acetylacetone peroxide, methylethylketone peroxide and cyclohexanone peroxide.
  • Further examples of the cold hardeners are amine-based accelerators, such as dimethyl aniline and diethylenaminetetracetate, in combination with benzoyl peroxide. As suggested by the name, cold hardeners do not require any heating to form radicals to start the polymerization in the second step.
  • the polymerization initiator does preferably not contain any metal. If the initiator contains any metal, the metal content in the coal-like material is adjusted to preferably not more than 0.5 wt%, more preferably not more than 0.1 wt%.
  • the reaction temperature can be kept much lower in the second step of the process of the invention in comparison to the prior art such as US 2008/0006518 Al.
  • the reaction temperature in the second step can be lower than in the first step. This allows for carrying out the process in less elaborate equipment, e.g. in a simple autoclave and has also significant benefits in terms of the reproducibility of the process and the quality control of the end product.
  • the polymerization i.e. carbonization to the coal-like material will proceed much quicker, e.g. by a factor of 3 to 10.
  • the reaction temperature in the second step can be in the range of 140 to 220 0 C, preferably it is 170 to 210 0 C, and more preferably 180 to 200 0 C.
  • the temperature in the second step is below the temperature in the first step.
  • the reaction mixture may be heated to a temperature in the range of 210 to 250 0 C in the first step, and to a temperature in the range of 170 to below (i.e. not including) 210 0 C, especially to 180 to 200 0 C in the second step.
  • the reaction temperature in the first step may be 220 to 250 0 C, and in the second step to 170 to 210 0 C.
  • the polymerization in the second step may be finished for instance within 1 to 3 hours. That is, within that time frame, a coal-like material of reproducible quality can be obtained.
  • the reaction can be carried out longer or shorter if desired.
  • the process according to the present invention is preferably carried out in a pressure resistant reactor, e.g. an autoclave or an extruder. Due to the water in the reaction mixture, there will be a pressure increase upon heating. As the hydrothermal carbonization reaction is exothermic, external heating may no longer be necessary, once the reaction, e.g. in the first step, has started, provided the thermal insulation of the reactor or reactors is sufficient.
  • the reaction temperature is meant to refer to the temperature, more specifically the average temperature, inside the reaction mixture, which can be measured with a thermocouple. Consequently, it is readily possible to control the reaction temperature to lie within the desired range by heating or cooling the reactor, as appropriate.
  • the solid phase comprised or consisting of the coal-like material can be separated from the reaction mixture, e.g. by filtration or decantation, preferably by filtration, while a liquid phase will remain.
  • this separation in particular the filtration can take place at the elevated temperatures of the second reactor, thus allowing an advantageous heat management of the reaction system. Then, the coal-like material can be dried.
  • the residual liquid phase obtained in the separation subsequent to step (ii) can be reused in the hydrothermal carbonisation process of the invention with particular benefit.
  • the above liquid phase which preferably contains > 80 wt%, more preferably > 90 wt% of water can be oxidized to obtain an oxidized liquid phase.
  • This can be done with any oxidizing agent, as long as this has a suitable oxidation potential to effect the oxidations as outlined hereinafter, and as long as the oxidizing agent or the reaction products thereof does not interfere with the further uses of the (oxidized) liquid phase as detailed below.
  • useful oxidizing agents are, without limitation, oxygen, hydrogen peroxide, percarbonate, and percarbonic acids.
  • the oxidizing agent is an oxygen-containing gas, which is preferably air.
  • the oxygen-containing gas such as air
  • the oxidation of the liquid phase can be effected by bubbling the gas through the liquid phase, stirring the liquid phase in an atmosphere of the gas or by allowing the liquid phase to stand in the presence of the gas.
  • the reaction mixture obtained in the second step which contains the liquid (aqueous) phase, rather than the (separated) liquid phase as such is oxidized, and the oxidized liquid phase is subsequently separated from the solid phase of the coal- like material in the reaction mixture.
  • the liquid phase in the mixture obtained in the second step contains e.g. ethers and ketones (such as laevulic acid) , which can be converted into the corresponding peroxides through the oxidation.
  • the peroxides are ketone peroxides, such as hydroxyacetone peroxides. These (hydro) peroxides can be recycled to the second step of the reaction, and be used as a polymerization initiator.
  • the liquid phase obtained in the second step can also be recycled to the first step, where these acids will be effective in accelerating the activation, in particular the disintegration as detailed above. If desired, the liquid phase obtained in the second step can be subjected to oxidation, as explained above, prior to recycling to the first step.
  • the recycling of the liquid phase to the first step also covers the embodiment where it is recycled to the mixing unit (to be further explained hereinafter) from which it will be transferred to the reactor in which the step (i) is to be carried out.
  • the optionally oxidized liquid phase preferably is still hot (e.g. it has a temperature of e.g. 50 - 220 0 C, preferably 90 -220 0 C, most preferably 140 - 180 0 C) when it is introduced in the reaction mixture of the first step and/or the second step.
  • the separated liquid (aqueous) phase from the second step ⁇ with or without oxidation) to admix it to the biomass prior to or during the first step of the hydrothermal carbonization process of the invention has a number of benefits.
  • the water content (and hence also the viscosity) of the reaction mixture in the first step can be optimally adjusted.
  • the heat included in the separated liquid phase can be reused in the process.
  • the liquid phase of the reaction mixture in the second step is divided into two parts, one of which is recycled (with or without oxidation) to the first step for pH management, and the second of which is recycled (after oxidation) to the second step to make up for consumed polymerization initiator.
  • the liquid phase from the second step may be subjected to the oxidation prior to dividing this into the above two parts.
  • the caloric heat can be handled efficiently, when the respective parts of the liquid phase are recycled when still hot.
  • the above recycling is particularly advantageous in a continuous flow system. Generally speaking, the above recycling allows for a minimization of side products and an optimization of the carbon yield in the hydrothermal carbonization process of the invention.
  • aqueous liquid phase of the second step for process reasons (both, as a carrier of heat and of chemically active components) is also beneficial from the point of view of sustainability .
  • Side products in the water phase i.e. the aqueous liquid phase
  • the equilibrium reactions under HTC conditions ensure that the yield of coal- like material is increased.
  • bringing the reaction water (i.e. the aqueous liquid phase) into the reaction multiple times has a beneficial influence on both the reaction kinetics as well as the carbonization yield, i.e. the yield of the coal -like material.
  • the two-step process of the present invention in which the first step is preferably characterized by higher temperature, shorter residence time, higher reaction viscosity (due to the raw biomass) , and higher technical demands, and in which the second step is preferably characterized by comparably longer residence time, lower temperatures and pressures, and a more passive reaction handling also exhibits many processing advantages.
  • the reactor in which the first step is to take place, which step, due to the preferably higher temperature and pressure, is more demanding from a process engineering point of view than the second, can be kept rather small, which is safer and moreover gives better heat transfer.
  • the reactor for carrying out the first step can be an extruder.
  • Extruders allow very high pressures of up to 700 bars, temperatures of up to 400 0 C, are made for viscous starting materials, are regarded as very reliable and safe. Moreover, extruders allow effective and rapid heating and the injection of additional reactants at desired positions.
  • the temperature of the reaction mixture containing the activated biomass is reduced downstream, e.g. at the end of the extruder to the desired reaction temperature of the second step, making use of an efficient heat exchanger, and the heat is used for the preheating of the biomass to be subjected to the first step.
  • the second reaction step can be carried out in a cascade of smaller reactors, which improves the residence time within the second step and gives an improved coal-like material.
  • Reference numeral 1 denotes a (raw) biomass storage vessel.
  • the biomass contained in the vessel 1 has a suitable particle size, e.g. in the range of 0.1 to 20 mm.
  • the biomass is fed to a mixing unit 2 where it is mixed with further ingredients such as water and acid to give a reaction mixture.
  • a stream 11 of the (aqueous) liquid phase separated in the separating unit 6 is recycled to the mixing unit 2 to provide at least part of the water and acid.
  • the stream of the aqueous liquid 11 (comprising acids) is mixed with the biomass in the mixing unit 2 without adding any further ingredients.
  • the separated liquid phase 11 preferably has a temperature of 140 to 220 0 C.
  • the reaction mixture obtained in the mixing unit 2 is then transferred to the reactor 3 in which the step (i) is carried out.
  • the reactor 3 is preferably an extruder as detailed above.
  • the reaction temperature T ⁇ may be between 190 and 270 0 C.
  • the reaction mixture comprising activated biomass obtained in the reactor 3 is then transported through a heat exchanger 4, from which the heat energy 8 can be recycled to the reactor 3.
  • the reaction mixture comprising activated biomass leaving the heat exchanger 4 is transferred to the reactor 5 for carrying out the polymerization step (ii) .
  • the reactor 5 is a pressure vessel, e.g. an autoclave. Preferably, it is provided with stirring means, which are schematically shown in the figure.
  • the internal temperature in the reactor 5 may be between 140 and 220 0 C.
  • a polymerization initiator may be added from the external ⁇ not shown) .
  • oxidized aqueous liquid phase 10 separated in the separating unit 6 and containing suitable peroxides is fed along with the reaction mixture comprising activating biomass to the reactor 5.
  • the reaction mixture comprising coal-like material obtained in the step (ii) is transferred from the reactor 5 to the separating unit (e.gr. filtration unit) 6, in which it is separated into a solid phase of the coal-like material 12, and an (aqueous) liquid phase 9.
  • the liquid phase 9 is split into two parts.
  • the first part is recycled as stream 11 (preferably having a temperature between 140 and 220 0 C) to the mixing unit 2.
  • the second part is oxidized by adding a suitable oxidizing agent from the oxidizing unit 7 to obtain species in the oxidized liquid phase 10 which can act as a polymerization initiator and can as such be recycled to the reactor 5 as detailed above.
  • the present invention relates to the coal- like material obtained or obtainable by the process of the invention as such which is preferably characterized by the physical characteristics, in particular the carbon content and the calorific value as detailed above.
  • the present invention will be further understood from the following examples, which are given by way of illustration and must not be construed in a limiting sense.
  • the carbon content of the materials was determined with a Vario Micro analyzer (Elementar Analy ⁇ ensysteme, Hanau, Germany) , and the calorific value of the materials was measured in accordance with BGS RAL- GZ 724.
  • the product After cooling and opening the autoclave, the product is separated into a solid phase ⁇ containing the hydrothermal coal) and a liquid phase.
  • hydrothermal coal which contains 68 wt% carbon and can be pulverized by hand.
  • the calorific value of the coal is 25 kJ/g.
  • Example 2 The liquid phase separated from the reaction mixture in Example 2, while still warm ⁇ 60 0 C) , is bubbled with air to obtain an oxidized liquid phase. Then, Example 2 is repeated except for using 200 ml of the thus-obtained oxidized liquid phase in place of the FeCl3 ⁇ 6 H2O and H2O2 • A product is obtained which is, within the measurement accuracy, the same as that obtained in Example 2.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Processing Of Solid Wastes (AREA)
  • Carbon And Carbon Compounds (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
PCT/EP2009/054602 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation WO2009127727A1 (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
US12/988,193 US20110056125A1 (en) 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation
BRPI0911421A BRPI0911421A2 (pt) 2008-04-17 2009-04-17 processo para conversão de biomassa em material semelhante a carvão usando carbonização hidro-térmica
CA2737596A CA2737596A1 (en) 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation
EP09733412A EP2274405A1 (en) 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation
AU2009237607A AU2009237607A1 (en) 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation

Applications Claiming Priority (4)

Application Number Priority Date Filing Date Title
US4583308P 2008-04-17 2008-04-17
EP08007516 2008-04-17
EP08007516.1 2008-04-17
US61/045,833 2008-04-17

Publications (1)

Publication Number Publication Date
WO2009127727A1 true WO2009127727A1 (en) 2009-10-22

Family

ID=39494401

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/EP2009/054602 WO2009127727A1 (en) 2008-04-17 2009-04-17 Process for converting biomass to coal-like material using hydrothermal carbonisation

Country Status (7)

Country Link
US (1) US20110056125A1 (ru)
EP (1) EP2274405A1 (ru)
AU (1) AU2009237607A1 (ru)
BR (1) BRPI0911421A2 (ru)
CA (1) CA2737596A1 (ru)
RU (1) RU2010146037A (ru)
WO (1) WO2009127727A1 (ru)

Cited By (26)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2010124381A1 (en) * 2009-04-30 2010-11-04 Evegenetics Canada Inc. Preparation of biofuels and other useful products such as 5-(hydroxymethyl)-furfural
CN102140356A (zh) * 2010-01-29 2011-08-03 宝山钢铁股份有限公司 神府煤水热处理方法
WO2011117837A3 (en) * 2010-03-24 2012-03-08 Antacor Pte. Ltd. Method and device for treating solid-fluid mixtures
WO2011143380A3 (en) * 2010-05-12 2012-04-12 Heilmann Steven M Process for obtaining oils, lipids and lipid-derived materials from low cellulosic biomass materials
EP2130893A3 (de) * 2008-06-05 2012-05-09 TerraNova Energy GmbH Verfahren zum Herstellen von Kohle insbesondere von Kohleschlamm
EP2474591A1 (en) 2011-01-10 2012-07-11 CSL Carbon Solutions Ltd Synthesis of artificial humic matter by hydrothermal carbonization
EP2484434A1 (de) * 2011-02-05 2012-08-08 GRENOL IP GmbH Kontinuierliche arbeitender Hydrothermale Karbonisierung Reaktor
WO2013076362A1 (en) * 2011-11-21 2013-05-30 Kemira Oyj Method for treating biomass
DE102012002098A1 (de) 2012-02-06 2013-08-08 Eurofoam Deutschland Gmbh Hydrothermale Karbonisierung von Kunststoffmaterial
EP2653451A1 (en) 2012-04-20 2013-10-23 CS Carbon Solutions Method and apparatus for the treatment of process water from an organic material conversion process
US8715462B2 (en) 2009-04-30 2014-05-06 Alexis Fosse Mackintosh Process and apparatus for recycling coated paper products
EP2746231A1 (en) 2012-12-19 2014-06-25 CS Carbon Solutions Method and apparatus for the treatment of process water from a hydrothermal organic material conversion process
WO2014096544A1 (en) 2012-12-19 2014-06-26 Teknologian Tutkimuskeskus Vtt Process for the hydrothermal treatment of high molar mass biomaterials
EP2765178A1 (en) * 2013-02-07 2014-08-13 Arbaflame Technology AS Method of producing carbon-enriched biomass material
EP2835413A2 (de) 2013-08-07 2015-02-11 Eurofoam Deutschland GmbH Schaumstoffe Partikel eines kohleähnlichen Feststoffs, Verwendungen und Herstellungsverfahren
FR3027914A1 (fr) * 2014-11-04 2016-05-06 Degremont Procede de carbonisation hydrothermale d'une biomasse, et dispositif s'y rapportant
WO2017222462A1 (en) 2016-06-23 2017-12-28 C-Green Technology Ab Method for oxidation of a liquid phase in a hydrothermal carbonization process
EP3363881A1 (de) * 2017-02-20 2018-08-22 AVA Green Chemistry Development GmbH Verfahren zur durchführung einer hydrothermalen karbonisierungsreaktion
AU2016247571B2 (en) * 2015-04-13 2018-11-08 Renergi Pty Ltd Method of and system for producing solid carbon materials
WO2019125275A1 (en) * 2017-12-21 2019-06-27 C-Green Technology Ab Oxidation and subsequent hydrothermal carbonization of sludge
WO2019125274A1 (en) * 2017-12-21 2019-06-27 C-Green Technology Ab Hydrothermal carbonization of sludge including recycling of a wet-oxidized fraction.
WO2020112007A1 (en) * 2018-11-26 2020-06-04 C-Green Technology Ab Method and system for hydrothermal carbonization and wet oxidation of sludge
US10836666B2 (en) 2016-06-23 2020-11-17 C-Green Technology Ab Method for oxidation of a liquid phase in a hydrothermal carbonization process
US11117117B2 (en) 2017-07-13 2021-09-14 Board Of Trustees Of The University Of Arkansas Doped carbonaceous materials for photocatalytic removal of pollutants under visible light, making methods and applications of same
US11306209B2 (en) 2015-11-21 2022-04-19 Suncoal Industries Gmbh Particulate carbon material producible from renewable raw materials and method for its production
US11952494B2 (en) 2017-10-10 2024-04-09 Continental Reifen Deutschland Gmbh Sulfur-crosslinkable rubber mixture, vulcanizate of the rubber mixture, and vehicle tire

Families Citing this family (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10377954B2 (en) * 2010-11-09 2019-08-13 Board Of Regents Of The Nevada System Of Higher Education, On Behalf Of The University Of Nevada, Reno Method for wet torrefaction of a biomass
US20130004408A1 (en) 2011-06-30 2013-01-03 Rubal Dua Moderate Temperature Synthesis of Mesoporous Carbon
WO2014066097A1 (en) * 2012-10-23 2014-05-01 Old Dominion University Research Foundation Subcritical water assisted oil extraction and green coal production from oilseeds
US10442995B2 (en) 2013-03-15 2019-10-15 Gas Technology Institute Rapid production of hydrothermally carbonized biomass via reactive twin-screw extrusion
CN103566899B (zh) * 2013-11-06 2015-08-12 山东科技大学 一种农业秸秆的综合处理方法
US9695093B2 (en) 2014-06-11 2017-07-04 Alireza Shekarriz Hydrothermal conversion process
CN104741051A (zh) * 2015-03-27 2015-07-01 安徽农业大学 一种低温下制备糖基炭微球的方法
US9968904B2 (en) 2015-06-10 2018-05-15 Alireza Shekarriz Hydrothermal conversion process with inertial cavitation
WO2018204411A1 (en) * 2017-05-01 2018-11-08 Board Of Regents Of Nevada System Of Higher Education, On Behalf Of University Of Nevada, Reno Method for conversion of wet biomass to energy
CN111661834B (zh) * 2019-03-08 2023-06-23 深圳先进技术研究院 一种二维纳米碳的制备方法
CN213295246U (zh) * 2020-05-28 2021-05-28 中环世特能源工程(上海)有限公司 一种矩阵式集成布局的生物质炭化设备系统
CN112591734A (zh) * 2020-12-29 2021-04-02 陕西科技大学 一种基于纳米木质素原位生长的纳米碳球及其制备方法
CN116656388B (zh) * 2022-02-28 2024-04-16 深圳市海立方生物科技有限公司 湿生物质废弃物的共液碳化处理方法、装置及用途

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4425256A (en) * 1979-12-28 1984-01-10 Marcoal Chemical Industries Conversion of cellulose into activated charcoal
US5354345A (en) * 1989-08-29 1994-10-11 Minnesota Power And Light Reactor arrangement for use in beneficiating carbonaceous solids; and process
EP1857532A1 (en) 2005-01-24 2007-11-21 Osaka Industrial Promotion Organization Solid biomass and method for production thereof
DE102006038983A1 (de) * 2006-08-21 2008-02-28 Logos-Innovationen Gmbh Verfahren zur Herstellung von Trinkwasser aus atmosphärischer Luft

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3354438B2 (ja) * 1996-06-04 2002-12-09 株式会社荏原製作所 有機物を含有する水媒体の処理方法及び水熱反応装置
DE102007056170A1 (de) * 2006-12-28 2008-11-06 Dominik Peus Semikontinuierliches Verfahren zur Herstellung von Brennstoff aus Biomasse
DE102008058444B4 (de) * 2007-11-21 2020-03-26 Antacor Ltd. Verfahren und Verwendung einer Vorrichtung zur Herstellung von Brennstoffen, Humus oder Suspensionen davon

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4425256A (en) * 1979-12-28 1984-01-10 Marcoal Chemical Industries Conversion of cellulose into activated charcoal
US5354345A (en) * 1989-08-29 1994-10-11 Minnesota Power And Light Reactor arrangement for use in beneficiating carbonaceous solids; and process
EP1857532A1 (en) 2005-01-24 2007-11-21 Osaka Industrial Promotion Organization Solid biomass and method for production thereof
DE102006038983A1 (de) * 2006-08-21 2008-02-28 Logos-Innovationen Gmbh Verfahren zur Herstellung von Trinkwasser aus atmosphärischer Luft

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See also references of EP2274405A1 *

Cited By (50)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2130893A3 (de) * 2008-06-05 2012-05-09 TerraNova Energy GmbH Verfahren zum Herstellen von Kohle insbesondere von Kohleschlamm
US9683328B2 (en) 2009-04-30 2017-06-20 Eve Research Inc. Preparation of biofuels and other useful products such as 5-(hydroxymethyl)-furfural
WO2010124381A1 (en) * 2009-04-30 2010-11-04 Evegenetics Canada Inc. Preparation of biofuels and other useful products such as 5-(hydroxymethyl)-furfural
US8715462B2 (en) 2009-04-30 2014-05-06 Alexis Fosse Mackintosh Process and apparatus for recycling coated paper products
CN102140356A (zh) * 2010-01-29 2011-08-03 宝山钢铁股份有限公司 神府煤水热处理方法
WO2011117837A3 (en) * 2010-03-24 2012-03-08 Antacor Pte. Ltd. Method and device for treating solid-fluid mixtures
WO2011143380A3 (en) * 2010-05-12 2012-04-12 Heilmann Steven M Process for obtaining oils, lipids and lipid-derived materials from low cellulosic biomass materials
WO2012095408A1 (en) 2011-01-10 2012-07-19 Csl Carbon Solutions Ltd. Synthesis of artificial humic matter by hydrothermal carbonization
EP2474591A1 (en) 2011-01-10 2012-07-11 CSL Carbon Solutions Ltd Synthesis of artificial humic matter by hydrothermal carbonization
EP2484434A1 (de) * 2011-02-05 2012-08-08 GRENOL IP GmbH Kontinuierliche arbeitender Hydrothermale Karbonisierung Reaktor
WO2013076362A1 (en) * 2011-11-21 2013-05-30 Kemira Oyj Method for treating biomass
DE102012002098A1 (de) 2012-02-06 2013-08-08 Eurofoam Deutschland Gmbh Hydrothermale Karbonisierung von Kunststoffmaterial
WO2013117600A1 (de) 2012-02-06 2013-08-15 Eurofoam Deutschland Gmbh Hydrothermale karbonisierung von kunststoffmaterial
EP2653452A1 (en) 2012-04-20 2013-10-23 CS Carbon Solutions Apparatus and method for the treatment of process water from a hydrothermal organic material conversion process
EP2653451A1 (en) 2012-04-20 2013-10-23 CS Carbon Solutions Method and apparatus for the treatment of process water from an organic material conversion process
EP2746231A1 (en) 2012-12-19 2014-06-25 CS Carbon Solutions Method and apparatus for the treatment of process water from a hydrothermal organic material conversion process
WO2014096544A1 (en) 2012-12-19 2014-06-26 Teknologian Tutkimuskeskus Vtt Process for the hydrothermal treatment of high molar mass biomaterials
US10518245B2 (en) 2012-12-19 2019-12-31 Valmet Technologies Oy Process for the hydrothermal treatment of high molar mass biomaterials
EP2765178A1 (en) * 2013-02-07 2014-08-13 Arbaflame Technology AS Method of producing carbon-enriched biomass material
WO2014122163A1 (en) * 2013-02-07 2014-08-14 Arbaflame Technology As Method of producing carbon-enriched biomass material
CN105164235A (zh) * 2013-02-07 2015-12-16 拉巴弗拉默技术公司 生产富含碳的生物质材料的方法
JP2016511308A (ja) * 2013-02-07 2016-04-14 アーバフレイム テクノロジー エイ・エスArbaflame Technology AS 炭素を富化したバイオマス材料の製造方法
US10119088B2 (en) 2013-02-07 2018-11-06 Arbaflame Technology As Method of producing carbon-enriched biomass material
EP2835413A2 (de) 2013-08-07 2015-02-11 Eurofoam Deutschland GmbH Schaumstoffe Partikel eines kohleähnlichen Feststoffs, Verwendungen und Herstellungsverfahren
EP3287510A1 (fr) * 2014-11-04 2018-02-28 Suez International Procédé de carbonisation hydrothermale d'une biomasse, et dispositif s'y rapportant
AU2015341447B2 (en) * 2014-11-04 2020-02-27 Suez International Method for the hydrothermal carbonisation of a biomass and associated device
WO2016071808A1 (fr) * 2014-11-04 2016-05-12 Degremont Procede de carbonisation hydrothermale d'une biomasse, et dispositif s'y rapportant
US10287505B2 (en) 2014-11-04 2019-05-14 Suez International Method for the hydrothermal carbonisation of a biomass and associated device
FR3027914A1 (fr) * 2014-11-04 2016-05-06 Degremont Procede de carbonisation hydrothermale d'une biomasse, et dispositif s'y rapportant
AU2016247571B2 (en) * 2015-04-13 2018-11-08 Renergi Pty Ltd Method of and system for producing solid carbon materials
US10329490B2 (en) 2015-04-13 2019-06-25 Curtin University Method of and system for producing solid carbon materials
US11639444B2 (en) 2015-11-21 2023-05-02 Suncoal Industries Gmbh Hydrothermal treatment of renewable raw material
US11312864B2 (en) 2015-11-21 2022-04-26 Suncoal Industries Gmbh Particulate carbon material producible from renewable raw materials and method for its production
US11306209B2 (en) 2015-11-21 2022-04-19 Suncoal Industries Gmbh Particulate carbon material producible from renewable raw materials and method for its production
US10836666B2 (en) 2016-06-23 2020-11-17 C-Green Technology Ab Method for oxidation of a liquid phase in a hydrothermal carbonization process
WO2017222462A1 (en) 2016-06-23 2017-12-28 C-Green Technology Ab Method for oxidation of a liquid phase in a hydrothermal carbonization process
EP3954752A1 (en) 2016-06-23 2022-02-16 C-Green Technology AB Method for oxidation of a liquid phase in a hydrothermal carbonization process
EP3363881A1 (de) * 2017-02-20 2018-08-22 AVA Green Chemistry Development GmbH Verfahren zur durchführung einer hydrothermalen karbonisierungsreaktion
US11117117B2 (en) 2017-07-13 2021-09-14 Board Of Trustees Of The University Of Arkansas Doped carbonaceous materials for photocatalytic removal of pollutants under visible light, making methods and applications of same
US11952494B2 (en) 2017-10-10 2024-04-09 Continental Reifen Deutschland Gmbh Sulfur-crosslinkable rubber mixture, vulcanizate of the rubber mixture, and vehicle tire
JP2021507806A (ja) * 2017-12-21 2021-02-25 シー − グリーン テクノロジー エービー 湿式酸化された画分のリサイクルを含む汚泥の水熱炭化
US20210078890A1 (en) * 2017-12-21 2021-03-18 C-Green Technology Ab Oxidation and Subsequent Hydrothermal Carbonization of Sludge
CN111492042B (zh) * 2017-12-21 2022-04-15 C-绿色科技公司 包括使湿氧化部分再循环的污泥水热碳化
WO2019125274A1 (en) * 2017-12-21 2019-06-27 C-Green Technology Ab Hydrothermal carbonization of sludge including recycling of a wet-oxidized fraction.
WO2019125275A1 (en) * 2017-12-21 2019-06-27 C-Green Technology Ab Oxidation and subsequent hydrothermal carbonization of sludge
JP7209725B2 (ja) 2017-12-21 2023-01-20 シー - グリーン テクノロジー エービー 湿式酸化された画分のリサイクルを含む汚泥の水熱炭化
CN111492042A (zh) * 2017-12-21 2020-08-04 C-绿色科技公司 包括使湿氧化部分再循环的污泥水热碳化
US11999921B2 (en) 2017-12-21 2024-06-04 C-Green Ab Hydrothermal carbonization of sludge including recycling of a wet-oxidized fraction
WO2020112007A1 (en) * 2018-11-26 2020-06-04 C-Green Technology Ab Method and system for hydrothermal carbonization and wet oxidation of sludge
US11724952B2 (en) 2018-11-26 2023-08-15 C-Green Technology Ab Method and system for hydrothermal carbonization and wet oxidation of sludge

Also Published As

Publication number Publication date
AU2009237607A1 (en) 2009-10-22
CA2737596A1 (en) 2009-10-22
EP2274405A1 (en) 2011-01-19
US20110056125A1 (en) 2011-03-10
BRPI0911421A2 (pt) 2017-05-23
RU2010146037A (ru) 2012-05-27

Similar Documents

Publication Publication Date Title
US20110056125A1 (en) Process for converting biomass to coal-like material using hydrothermal carbonisation
Kambo et al. Process water from the hydrothermal carbonization of biomass: a waste or a valuable product?
US8481642B2 (en) Process for the preparation of hydrothermal hybrid material from biomass, and hydrothermal hybrid material obtainable by the process
US8637718B2 (en) Biomass to biochar conversion in subcritical water
Rollag et al. Pretreatments for the continuous production of pyrolytic sugar from lignocellulosic biomass
KR102125536B1 (ko) 탄소 농축 바이오매스 재료의 제조 방법
Wang et al. Co-pyrolysis of lignin and polyethylene with the addition of transition metals-Part I: Thermal behavior and kinetics analysis
US20120042566A1 (en) Preparation of biofuels and other useful products such as 5-(hydroxymethyl)-furfural
Safarian Performance analysis of sustainable technologies for biochar production: A comprehensive review
Cheng et al. Hydrothermal carbonization of rape straw: Effect of reaction parameters on hydrochar and migration of AAEMs
Kim et al. The pyrolysis of waste mandarin residue using thermogravimetric analysis and a batch reactor
Liu et al. Technical progress and perspective on the thermochemical conversion of kitchen waste and relevant applications: A comprehensive review
Guo et al. Comparative investigation on thermal decomposition of powdered and pelletized biomasses: Thermal conversion characteristics and apparent kinetics
Wang et al. Co-pyrolysis of microwave-assisted acid pretreated bamboo sawdust and soapstock
Pyshyev et al. State of the art in the production of charcoal: A review
Ronsse Biochar production
Ingole et al. Microwave assisted pyrolysis of biomass: a review
Preradovic et al. Torrefaction: Process Review
CN110819367B (zh) 一种生物质的燃料品质的预测方法及其应用
US10428288B2 (en) Process for converting a biomass into at least one biochar
Rambli et al. Characterization of Sago-based Biochar as Potential Feedstock for Solid Fuel
US20130160355A1 (en) Method for Processing Solid and Liquid Wastes from the Production of Vegetable Oil
US20160289583A1 (en) Pelletized fuel products, methods, and apparatuses
Xu et al. Comparative study on the properties of wood vinegar prepared from the pretreated Chinese fir: Effect of hydrothermal parameters and hydrogen peroxide
Banga et al. Torrefaction of Biomass

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 09733412

Country of ref document: EP

Kind code of ref document: A1

DPE1 Request for preliminary examination filed after expiration of 19th month from priority date (pct application filed from 20040101)
NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 2009237607

Country of ref document: AU

WWE Wipo information: entry into national phase

Ref document number: 4197/KOLNP/2010

Country of ref document: IN

Ref document number: 2009733412

Country of ref document: EP

WWE Wipo information: entry into national phase

Ref document number: 12988193

Country of ref document: US

WWE Wipo information: entry into national phase

Ref document number: 2010146037

Country of ref document: RU

Ref document number: A201013537

Country of ref document: UA

ENP Entry into the national phase

Ref document number: 2009237607

Country of ref document: AU

Date of ref document: 20090417

Kind code of ref document: A

WWE Wipo information: entry into national phase

Ref document number: 2737596

Country of ref document: CA

ENP Entry into the national phase

Ref document number: PI0911421

Country of ref document: BR

Kind code of ref document: A2

Effective date: 20101018