WO1981000854A1 - Traitement de materiaux organiques dans de i'eau supercritique - Google Patents

Traitement de materiaux organiques dans de i'eau supercritique Download PDF

Info

Publication number
WO1981000854A1
WO1981000854A1 PCT/US1980/001214 US8001214W WO8100854A1 WO 1981000854 A1 WO1981000854 A1 WO 1981000854A1 US 8001214 W US8001214 W US 8001214W WO 8100854 A1 WO8100854 A1 WO 8100854A1
Authority
WO
WIPO (PCT)
Prior art keywords
water
toxic
organic
materials
feed
Prior art date
Application number
PCT/US1980/001214
Other languages
English (en)
Inventor
D Whitlock
Original Assignee
Modar Inc
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 Modar Inc filed Critical Modar Inc
Priority to AU64809/80A priority Critical patent/AU6480980A/en
Publication of WO1981000854A1 publication Critical patent/WO1981000854A1/fr

Links

Classifications

    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10G—CRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00—Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/02—Treatment of water, waste water, or sewage by heating
    • C02F1/025—Thermal hydrolysis

Definitions

  • the prior art has also converted organic liquids to fuels by reaction with water, as for example, by reforming petroleum fractions catalytically to methane and carbon dioxide by a reaction with steam at 20 to 40 atmospheres. This avoids the use of a high temperature heat source and has met with some success where it is desirable to convert organic liquids to gaseous products.
  • liquid or solid organic materials can be converted to high BTU gas with little or no formation of undesirable char or coke when the organic material is reacted with water at a temperature at or above the critical temperature of water and at or above the critical pressureof water to achieve the critical density of water as for example set forth in United States Patent 4,113,446.
  • feed material was indicated to be converted to gaseous products in an amount of about 8 to 10% after one hour in a batch autoclave.
  • 20 to 25% of the feed carbon could be gasified in relatively short times as for example 30 minutes.
  • the formation of char can easily be avoided and useful high BTU gas is produced.
  • organic feeds were not completely transformed to gaseous products having high fuel value even after substantial periods of time at supercritical conditions.
  • an organic material which can be solid or liquid is treated by reacting in water to restructure the organic material and form resulting organic material.
  • the feed organic material is admixed with water to form a reaction mixture for a time period while maintaining the water in the region of its critical density preferably by the use of a temperature at least as high as about the critical temperature of water and a pressure at least as high as about the critical pressure of water to form resulting more volatile organic material than the feed organic material which resulting material is selected from the group consisting essentially of non-toxic organic materials where the original feed material was toxic, and useful volatile organic liquids.
  • the useful volatile organic liquids are recovered in amounts of at least 25 weight percent of the feed organic material.
  • the organic material is a toxic material or a toxic material in at least trace amounts in a mixture as for example river water and the resulting product is a non- toxic material as for example cleansed water containing lower molecular weight organic materials which are non- toxic.
  • the original organic material is a solid or heavy liquid material and the resulting products are lower molecular weight volatile organic liquids which can be used as fuels or for other purposes.
  • the process is carried out by bringing the reacting temperature to at least 374°C rapidly and preferably substantially instantaneously to avoid the formation of char.
  • the resulting products may be safely discarded if no commercially useful products are formed.
  • the separation techniques for separating useful products from the reaction mixture include distillation, flashing, decanting and membrane separation. It is a feature of this invention that the liquid products formed are hydrophilic and can have volatilities such that they will distill off before water and thus be easily separated in distillation procedures.
  • volatile as used in this application with reference to organic liquids means organic products which have a vapor pressure no less than 1/10 that of water at any temperature in the range of 25°C to 374°C.
  • organic material is restructured in water to form different organic materials which include volatile organic liquids and in some cases, non- toxic organic materials which may or may not be volatile liquids.
  • the process can be carried out in batch or continuous operations.
  • the process can be carried out in an autoclave as described in U.S. Patent 4,113,446.
  • Continuous methods can be used where a reaction slurry or liquid mixture of the reactants and water is treated under heat and pressure.
  • a feed mixture of organic material to be treated is preferably brought to temperature of reaction as for example at least 374° C, quickly, as by adding it in a continuous stream to a flow of superheated water, heated for example to 600 to 900°C, to quickly and substantially instantaneously bring the organic material feed to temperature.
  • the quick heating of the feed minimizes or substantially eliminates char formation.
  • the reaction conditions are such that the organic material feed is used in an amount up to about 25 weight percent of water and preferably from about 5 to 10 weight percent of water.
  • Low concentrations may be used, as for example fractional percentages, in reforming toxic materials to non-toxic material as for example in the detoxification and purification of contaminated surface water or well water.
  • Catalysts can be used during the reaction to promote reforming and hydrogenation of organic materials as well as to facilitate simple breakdown of organic chains.
  • Representative suitable catalysts include nickel, molybdenum, cobalt, their oxides or sulfides, and noble metal catalysts such as platinum, palladium or the like or mixtures thereof either unsupported or supported on a base such as silica, alumina mixtures thereof and the like.
  • the reaction often preferably is carried out at the critical density of water which means that the temperature must be at least the critical temperature and the pressure at least the critical pressure of water.
  • Parameters at the near critical condition of water can also be used and should be considered the equivalent of exact critical condition.
  • the terms “substantially at its critical density”, “about its critical temperature” and “about its critical pressure” refer to water in the near critical region.
  • the near critical region or the term “in the region of the critical density of water” is encompassed by densities of from
  • pressures can be from 200 to
  • 2500 atmospheres and temperatures can be from 374°C to at least 450°C.
  • a critical temperature range of 374°C to 450°C and a critical density range of .3 to .55 grams per centimeter are preferred for use.
  • Toxic material which can be treated by reaction with water under critical conditions include those on the EPA toxic chemical list of toxic organic substances as for example:
  • toxic materials are those recognized as hazardous by the U.S. Environmental Protection Agency as for example those set out in EPA publication EPA-560/11-79-001 entitled Test Data Development Standards: Chronic Health Effects Toxic Substances Control Act; Section 4.
  • the reaction mixture after reaction can then be discarded safely.
  • the resulting materials can be removed as by biological oxidation, activated carbon adsorption and the like before discarding or reusing the remaining water.
  • the non-toxic products which result from reformation of the toxic organic starting materials can be used for commercial purposes. For example, volatile liquids formed can be used as fuels. It is found that since toxicity is highly structure-specific, simple altering of one or more chemical bonds in many organic toxic materials results in products which are non-toxic and which can be safely disposed of.
  • the non-toxic starting materials which are to be reformed by the process of this invention for use as fuels or for other commercial purposes can be a wide variety of staring materials.
  • Solid organics include coal or organic waste materials, cellulose, waxes, coal tars, shale, wood products including trees, leaves, bark and the like.
  • Liquid organic materials including aryl or acyl hydrocarbons such as petroleum fractions up to and including asphalt fractions, aromatic hydrocarbons, sugars, black liquor from pulping of wood, green liquor used to pulp, organic acids, alcohols, aldehydes, ketones, amines, mixtures thereof and the like can be used.
  • the reaction is preferably effected by continuously intimately contacting the organic feed material with water.
  • solid organic material such as coal or organic waste material
  • the solid particles can be small and in the order of from submicron size to about 1 cm. Larger particles can be employed in some cases.
  • a flow reactor was used with a one weight percent solution of glucose in water.
  • the feed solution was heated rapidly to supercritical conditions by pumping to 315 atmospheres and then passing the mixture through a feed preheater, which was constructed of 10 feet of 3/32 inch, inside diameter, stainless steel tubing immersed in a molten lead bath at 380°C. A residence time of less than 20 seconds was required to reach 374°C; within one minute, the feed was brought to essentially the temperature of the lead bath.
  • the mixture was maintained at the supercritical conditions of 315 atmospheres and 380°C for a residence time of about 7 to 11 minutes in a reactor consisting of a ten foot section of 5/16 inch, inside diameter, stainless steel tubing, which was also maintained at constant temperature by immersion in the molten lead bath.
  • the products were then passed through a water-cooled heat exchanger to bring the resulting mixture to room temperature and then to a throttling valve to bring the mixture to atmospheric pressure. Liquid and vapor phases were separated and the flow rates of each of these phases was measured. Samples of the vapor phase were analyzed by gas chromatography and the liquid phase was analyzed for total carbon. The results are shown in Tables 1 and 2.
  • FIG. 1 illustrates a preferred flow diagram for a continuous process of reforming solid organic material to form liquid fuels and chemicals as shown in FIG. 1 at 10.
  • the supercritical water reformer is noted at 21 and is preferably sized as a tubular reactor with a flow therethrough such that the material to be reformed spends only from seconds to minutes under supercritical conditions to rapidly dissolve and disperse the solid matter in the feed and rapidly break down high molecular weight components into gases and volatile liquids such as hydrogen, carbon monoxide, methane, carbon dioxide and other reformed lower molecular weight volatile liquid organic compounds.
  • Portions of the products produced may be oxidized within the overall processing scheme and utilized for internal energy requirements as in heating water to supercritical conditions.
  • FIG. 1 shows a wood chip process where a feed of wood chips is fed to a slurry tank 20 and suspended in water.
  • Feed pump 19 pumps the feed to a supercritical water reformer 21 which also receives super heated, supercritical water at high temperature so that the cold feed is instantly heated to supercritical conditions as previously described.
  • a heat exchanger 22 is positioned in the line from the reformer 21 so as to heat combustion air going to the furnace 11 which in turn heats the water to supercritical conditions for use in the reformer 21.
  • the flow from the reformer 21, is brought to a subcritical flashing unit 17 which removes gaseous products to a gas expander 16 and in turn uses these gases in the heating process of the furnace 11.
  • the flashing unit 17 is maintained somewhat below the critical temperature of the aqueous solution, although the pressure may be above the critical pressure of water. Typically, the temperature may be 300 to 350°C in flashing unit 17.
  • Organic liquids and water are taken through a liquid expander 18 where liquids are passed to a steam stripper 12 and condenser 13 arrangement which takes off organic liquids for use as fuel or chemicals.
  • Off gases from the superheater 11 are passed to a boiler 14 which acts to aid in the stripping occurring in the stripper 12 while recycled water passes to water pump 15 for passage to the water heater with some water passing to the feed slurry tank.
  • the feed can be mixed to the proper proportion in the feed slurry tank bearing in mind the additional superheated water that will be added in the reformer. No predrying of the feed is necessary.
  • the slurry can be pressurized and heated to supercritical conditions very rapidly to avoid char formation. Heating can be obtained by mixing the feed with the superheated, supercritical water at 600 to 900°C or by heating along the line leading from the slurry tank to the reformer. In all cases, short residence times of up to 15 minutes are preferably maintained in the supercritical water reactor.
  • FIG. 2 illustrates the processing of a slurry such as black liquor from pulping which contains relatively high concentrations of inorganic materials as well as organic materials.
  • Black liquor from the holding tank 31 is pumped through pump 32 to the super- critical water reformer 33 which is maintained at near critical conditions and causes rapid breakdown of organics.
  • the reformer 33 passes the reaction products to the heat exchanger 35 where heat is taken off to heat water passing to the supercritical water superheater 41 which water is in turn used in the reformer.
  • Combustion air is used to heat the water in the superheater 41 along with combustible gases and volatile organics obtained from a flash drum number 2 at 40 with the oil phase from the flash drum passing to fuel storage.
  • Flash drum number 1 at 38 is maintained at temperatures and pressures below the critical conditions of water, where volatile organic material, gaseous products, and steam can be collected overhead. These conditions are typically in the range of 250 to 350°C and 30 to 150 atmospheres.
  • the inorganic solution can be used to recover sodium and sulfur so as to obtain an acceptable green liquor which is subsequently to be mixed with wood feed.
  • the temperature and pressure of the overhead steam from flash drum number 1 are reduced further and fed to flash drum number 2 at 40 through a heat exchanger 37.
  • the conditions in flash drum number 2 at 40 are typically ambient temperature to
  • the aqueous phase con taining hydrophilic organics is taken from the flash drum number 2 passed through a booster 39 heat exchanger 37 and 35 and back to the superheater 41. It is repressurized reheated and superheated before recycled to the supercritical water heater 41.
  • the separation of the volatile liquid organics formed during the reactions with water at the critical density can be carried out under varying conditions.
  • steam stripping at atmospheric pressure can be used to remove the volatile organic liquids from the water in the reaction vessel after the reaction or in a subsequent vessel in processing.
  • Distillation in a distillation tower can be carried out at pressures ranging from atmospheric to on the order of a 150 atmospheres to separate the liquid organic products from the water.
  • the volatile organics can be collected in the vapor phase along with water to leave volatile organic residuals in the liquid phase after the reaction as for example at temperatures of from 250 to 350°C at 30 to 150 atmospheres.
  • Flashing can be .used at temperature in the range of 300 to 350°C to take off gaseous products.
  • Membrane separation such as reverse osmosis, can be used to separate volatile organic liquids.
  • the volatile organic liquids being highly hydrophilic, require the separation step and are produced in sufficient quantity to make separation feasible.
  • the volatile organic liquids are produced in quantities at least as high as 25% but more preferably at least as high as 50% of the original organic feed.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Water Supply & Treatment (AREA)
  • Physics & Mathematics (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Wood Science & Technology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Thermal Sciences (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

Des materiaux organiques sont traites dans de l'eau dans la zone de densite critique de l'eau pour restructurer les materiaux organiques d'alimentation pour former des materiaux organiques comprenant des materiaux non toxiques a partir de materiaux de depart toxiques et des liquides organiques volatiles utiles. Des materiaux solides et des materiaux liquides visqueux sont restructures pour former des combustibles liquides ou autres produits liquides utiles. Des materiaux toxiques sont restructures pour etre rendus non toxiques dans divers systeme de traitement.
PCT/US1980/001214 1979-09-27 1980-09-22 Traitement de materiaux organiques dans de i'eau supercritique WO1981000854A1 (fr)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AU64809/80A AU6480980A (en) 1979-09-27 1980-09-22 Treatment of organic material in supercritical water

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US7953579A 1979-09-27 1979-09-27
US79535 1979-09-27

Publications (1)

Publication Number Publication Date
WO1981000854A1 true WO1981000854A1 (fr) 1981-04-02

Family

ID=22151161

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/US1980/001214 WO1981000854A1 (fr) 1979-09-27 1980-09-22 Traitement de materiaux organiques dans de i'eau supercritique

Country Status (1)

Country Link
WO (1) WO1981000854A1 (fr)

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5009745A (en) * 1990-10-12 1991-04-23 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans from secondary fibers using supercritical CO2 extraction
US5009746A (en) * 1990-10-12 1991-04-23 Kimberly-Clark Corporation Method for removing stickies from secondary fibers using supercritical CO2 solvent extraction
US5074958A (en) * 1990-10-12 1991-12-24 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans and stickies from secondary fibers using supercritical propane solvent extraction
US5075017A (en) * 1990-10-12 1991-12-24 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans from paper mill sludge
US5213660A (en) * 1990-10-12 1993-05-25 Kimberly-Clark Corporation Secondary fiber cellulose product with reduced levels of polychlorinated dibenzodioxins and polychlorinated dibenzofurans
US5746926A (en) * 1996-03-22 1998-05-05 Sri International Method for hydrothermal oxidation of halogenated organic compounds with addition of specific reactants
EP0850666A1 (fr) * 1996-12-13 1998-07-01 Director-General Of The Agency Of Industrial Science And Technology Méthode pour la décomposition des polychlorobiphényles
US5842289A (en) * 1995-11-13 1998-12-01 Manufacturing And Technology Conversion International, Inc. Apparatus for drying and heating using a pulse combustor
EP0898985A1 (fr) * 1997-08-20 1999-03-03 Kabushiki Kaisha Toshiba Procédé et dispositif de traitement des déchets sous des conditions supercritiques
ES2190824A1 (es) * 1998-11-03 2003-08-16 Univ Cordoba Extractor continuo para sustancias oleaginosas, solidas y liquidas, basado en el uso de agua sobrecalentada.
US20120289695A1 (en) * 2009-02-11 2012-11-15 Southern Illinois University Carbondale Production of organic materials using oxidative hydrothermal dissolution method
RU2604726C2 (ru) * 2011-06-03 2016-12-10 Саутерн Иллинойс Юниверсити Карбондейл Производство органических материалов с использованием способа окислительного гидротермического растворения
CN110790467A (zh) * 2019-10-12 2020-02-14 西安交通大学 一种用于超临界水氧化处理系统的加热系统及控制方法

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3148227A (en) * 1961-05-04 1964-09-08 Crown Zellerbach Corp Preparation of unsaturated hydrocarbons from oxygen-containing organic materials
US3715195A (en) * 1971-06-30 1973-02-06 Texaco Inc Multihydrotorting of coal
US3890113A (en) * 1973-06-25 1975-06-17 Texaco Inc Production of methane
US3919113A (en) * 1969-11-21 1975-11-11 Texaco Development Corp Oxo-synthesis gas
US3926583A (en) * 1967-06-12 1975-12-16 Haldor Topsoe As Process for the catalytic steam reforming of hydrocarbons
US3929431A (en) * 1972-09-08 1975-12-30 Exxon Research Engineering Co Catalytic reforming process
US4113446A (en) * 1975-07-22 1978-09-12 Massachusetts Institute Of Technology Gasification process
US4145188A (en) * 1976-11-22 1979-03-20 Mobil Oil Corporation Liquefaction of solid organic wastes

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3148227A (en) * 1961-05-04 1964-09-08 Crown Zellerbach Corp Preparation of unsaturated hydrocarbons from oxygen-containing organic materials
US3926583A (en) * 1967-06-12 1975-12-16 Haldor Topsoe As Process for the catalytic steam reforming of hydrocarbons
US3919113A (en) * 1969-11-21 1975-11-11 Texaco Development Corp Oxo-synthesis gas
US3715195A (en) * 1971-06-30 1973-02-06 Texaco Inc Multihydrotorting of coal
US3929431A (en) * 1972-09-08 1975-12-30 Exxon Research Engineering Co Catalytic reforming process
US3890113A (en) * 1973-06-25 1975-06-17 Texaco Inc Production of methane
US4113446A (en) * 1975-07-22 1978-09-12 Massachusetts Institute Of Technology Gasification process
US4145188A (en) * 1976-11-22 1979-03-20 Mobil Oil Corporation Liquefaction of solid organic wastes

Cited By (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5009746A (en) * 1990-10-12 1991-04-23 Kimberly-Clark Corporation Method for removing stickies from secondary fibers using supercritical CO2 solvent extraction
US5074958A (en) * 1990-10-12 1991-12-24 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans and stickies from secondary fibers using supercritical propane solvent extraction
US5075017A (en) * 1990-10-12 1991-12-24 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans from paper mill sludge
US5213660A (en) * 1990-10-12 1993-05-25 Kimberly-Clark Corporation Secondary fiber cellulose product with reduced levels of polychlorinated dibenzodioxins and polychlorinated dibenzofurans
US5009745A (en) * 1990-10-12 1991-04-23 Kimberly-Clark Corporation Method for removing polychlorinated dibenzodioxins and polychlorinated dibenzofurans from secondary fibers using supercritical CO2 extraction
US5842289A (en) * 1995-11-13 1998-12-01 Manufacturing And Technology Conversion International, Inc. Apparatus for drying and heating using a pulse combustor
US5746926A (en) * 1996-03-22 1998-05-05 Sri International Method for hydrothermal oxidation of halogenated organic compounds with addition of specific reactants
US6124519A (en) * 1996-12-13 2000-09-26 Director-General Of Agency Of Industrial Science And Technology Method of decomposing polychlorobiphenyls
EP0850666A1 (fr) * 1996-12-13 1998-07-01 Director-General Of The Agency Of Industrial Science And Technology Méthode pour la décomposition des polychlorobiphényles
EP0898985A1 (fr) * 1997-08-20 1999-03-03 Kabushiki Kaisha Toshiba Procédé et dispositif de traitement des déchets sous des conditions supercritiques
US6090291A (en) * 1997-08-20 2000-07-18 Kabushiki Kaisha Toshiba Waste processing method and waste processing apparatus
EP1325766A2 (fr) * 1997-08-20 2003-07-09 Kabushiki Kaisha Toshiba Procédé et dispositif de traitement des déchets sous des conditions supercritiques
EP1325766A3 (fr) * 1997-08-20 2003-07-16 Kabushiki Kaisha Toshiba Procédé et dispositif de traitement des déchets sous des conditions supercritiques
ES2190824A1 (es) * 1998-11-03 2003-08-16 Univ Cordoba Extractor continuo para sustancias oleaginosas, solidas y liquidas, basado en el uso de agua sobrecalentada.
US20120289695A1 (en) * 2009-02-11 2012-11-15 Southern Illinois University Carbondale Production of organic materials using oxidative hydrothermal dissolution method
US10023512B2 (en) * 2009-02-11 2018-07-17 Southern Illinois University Carbondale Production of organic materials using oxidative hydrothermal dissolution method
RU2604726C2 (ru) * 2011-06-03 2016-12-10 Саутерн Иллинойс Юниверсити Карбондейл Производство органических материалов с использованием способа окислительного гидротермического растворения
CN110790467A (zh) * 2019-10-12 2020-02-14 西安交通大学 一种用于超临界水氧化处理系统的加热系统及控制方法

Similar Documents

Publication Publication Date Title
WO1981000855A1 (fr) Traitement de materiaux organiques dans de l'eau supercritique
CA1166771A (fr) Methode d'oxydation de matieres organiques sous eau supercritique
US4543190A (en) Processing methods for the oxidation of organics in supercritical water
Jarana et al. Supercritical water gasification of industrial organic wastes
TW388721B (en) Process for treatment of effluent gas stream and for production of aromatic polycarboxylic acid and aromatic carboxylic acids
WO1981000854A1 (fr) Traitement de materiaux organiques dans de i'eau supercritique
US6180845B1 (en) Transforming biomass to hydrocarbon mixtures in near-critical or supercritical water
Schmieder et al. Hydrothermal gasification of biomass and organic wastes
Qian et al. Treatment of sewage sludge in supercritical water and evaluation of the combined process of supercritical water gasification and oxidation
RU2526254C2 (ru) Способ растворения угля, биомассы и других твердых органических материалов в перегретой воде
JPH05504093A (ja) 水の臨界超過温度で物質を酸化させる方法
JPS60231792A (ja) 清澄汚泥から炭火水素を製造する方法
DK179687B1 (en) High pressure treatment system separation system
Casademont et al. Hydrogen production by catalytic conversion of olive mill wastewater in supercritical water
JPH11172262A (ja) セルロース系バイオマスのガス化方法
CA1170831A (fr) Methodes de traitement pour l'oxydation de produits organiques dans de l'eau a l'etat supercritique
AU6571680A (en) Treatment of organic material in supercritical water
AU6480980A (en) Treatment of organic material in supercritical water
US4294720A (en) Process for the preparation of gas mixtures
Modell Detoxification and disposal of hazardous organic chemicals by processing in supercritical water
WO2001040406A1 (fr) Procede de recuperation d'hydrocarbures issus d'un materiau contenant du carbone
Lee et al. Conversion of municipal sludge to oil
Kıpçak et al. Catalytic gasification of olive mill wastewater as a biomass source under supercritical conditions
Jarana et al. Hydrothermal gasification treatment for hydrogen generation from organic wastes
Pennisi Water, water everywhere

Legal Events

Date Code Title Description
AK Designated states

Designated state(s): AU BR CH DE GB JP NL SE

WA Withdrawal of international application