WO2003074639A1 - Method for treating carbonaceous materials - Google Patents

Method for treating carbonaceous materials Download PDF

Info

Publication number
WO2003074639A1
WO2003074639A1 PCT/AU2003/000258 AU0300258W WO03074639A1 WO 2003074639 A1 WO2003074639 A1 WO 2003074639A1 AU 0300258 W AU0300258 W AU 0300258W WO 03074639 A1 WO03074639 A1 WO 03074639A1
Authority
WO
WIPO (PCT)
Prior art keywords
carbonaceous materials
acid
sulfur
hydrofluorosilicic
hydrofluorosilicic acid
Prior art date
Application number
PCT/AU2003/000258
Other languages
French (fr)
Inventor
Robert Lloyd
Original Assignee
Karalee Research Pty 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
Priority to EA200401152A priority Critical patent/EA006065B1/en
Priority to MXPA04008579A priority patent/MXPA04008579A/en
Application filed by Karalee Research Pty Ltd filed Critical Karalee Research Pty Ltd
Priority to US10/506,306 priority patent/US20060150474A1/en
Priority to CA002477882A priority patent/CA2477882A1/en
Priority to KR10-2004-7013851A priority patent/KR20040106285A/en
Priority to IL16383503A priority patent/IL163835A0/en
Priority to JP2003573093A priority patent/JP2005519017A/en
Priority to NZ535220A priority patent/NZ535220A/en
Priority to AU2003205451A priority patent/AU2003205451A1/en
Priority to EP03702221A priority patent/EP1483360A4/en
Priority to BR0308198-2A priority patent/BR0308198A/en
Priority to UA20041008008A priority patent/UA77769C2/en
Publication of WO2003074639A1 publication Critical patent/WO2003074639A1/en
Priority to IL163835A priority patent/IL163835A/en
Priority to NO20043674A priority patent/NO20043674L/en
Priority to AU2009202202A priority patent/AU2009202202A1/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
    • C10L9/00Treating solid fuels to improve their combustion
    • C10L9/02Treating solid fuels to improve their combustion by chemical means

Definitions

  • the invention relates to methods for treating carbonaceous materials to remove or substantially decrease the amount of non-carbonaceous impurities therein.
  • United States Patent No. 4,780,112 describes a process for treating carbon to reduce the ash therein.
  • the process involves treating the carbon with an aqueous solution of hydrofluorosilicic acid (H 2 SiF 6 ) and hydrofluoric acid (HF), whereby metal oxides in the carbon are converted to metal fluorides and/or metal fluorosilicates, from which carbon is then separated.
  • H 2 SiF 6 hydrofluorosilicic acid
  • HF hydrofluoric acid
  • the process described in United States Patent No. 4,780,112 is effective for removal of metal oxides from carbon, but the present inventor has surprisingly discovered that when carbon that includes sulfur-containing impurities is treated by the process of United States Patent No. 4,780,112, the purified carbon is still contaminated with sulfur.
  • the present inventor has surprisingly discovered that the remaining sulfur is present as elemental sulfur, which in some circumstances is visible when the carbon is viewed under a microscope.
  • the present inventor has discovered that the amount of sulfur- containing impurities in carbonaceous materials can be substantially decreased by a process which involves treating the carbonaceous materials with an aqueous solution of hydrofluorosilicic acid, or with an organic solvent capable of dissolving elemental sulfur.
  • a process for reducing the amount of sulfur-containing impurities in carbonaceous materials comprising (a) contacting the materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products, and (b) separating the reaction products from the carbonaceous materials.
  • a process for reducing the amount of sulfur-containing impurities in carbonaceous materials comprising treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and then contacting the carbonaceous materials with an organic solvent capable of dissolving elemental sulfur.
  • a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride
  • separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride and then contacting the carbonaceous materials with an organic solvent capable of dissolving elemental sulfur.
  • carbonaceous materials is to be understood to mean materials which consist predominantly of elemental carbon. Examples of carbonaceous materials include coal including brown coal, coke, lignite, anthracite, charcoal, graphite and the like.
  • the concentration of hydrofluorosilicic acid in the step of contacting the materials with an aqueous solution of hydrofluorosilicic acid under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products may be in the range of 27% to 37% (w/v or w/w or v/w).
  • the concentration of hydrofluorosilicic acid in the step of contacting the materials with an aqueous solution of hydrofluorosilicic acid under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products is typically in the range of 28% to 36%, more typically about 32%(w/v or w/w or v/w).
  • the process is usually carried out at atmospheric pressure, but the pressure can also be above or below atmospheric.
  • the temperature may be in the range 28 to 75°C. Typically, the temperature is in the range of 30 to 70 °C, more usually 30 to 40 °C.
  • the reaction time may be in the range 8 to 120 minutes.
  • the reaction time is typically from 10 to 100 minutes, more usually 15 to 30 minutes, still more usually 12 to 16 minutes.
  • the minimum quantity of aqueous hydrofluorosilicic acid employed is typically enough to enable the mixture of it and the carbonaceous materials to be stirred in the acid.
  • the carbonaceous materials are mixed with at least about twice their weight of the aqueous hydrofluorosilicic acid. More usually, the aqueous hydrofluorosilicic acid is present in an amount of from about 70% to 90% by weight, relative to the total weight of the mixture, still more usually about 70% to 80% by weight of the total weight of the mixture.
  • step (a) of the processes of the first and second embodiments of the invention many metal oxides and some metals present in the carbonaceous materials are converted, at least partially, into the corresponding metal fluorosilicates, with water being the other product.
  • metals or metal oxides converted to their fluorosilicates are nickel, aluminium, calcium, and mercury and their oxides.
  • Sulfur compounds present are converted, under the reaction conditions, to sulfur dioxide and/or sulfur tetrafluoride.
  • step (a) of the processes of the first and second embodiments of the invention relatively purified carbonaceous materials remain mixed with an aqueous solution containing dissolved metal fluorosilicates.
  • this mixture of carbonaceous materials and metal fluorosilicates may be filtered or centrifuged to separate the relatively purified carbonaceous materials.
  • the filtered relatively purified carbonaceous materials may be treated with further aqueous hydrofluorosilicic acid, typically having a concentration of 32% by weight of hydrofluorosilicic acid, to wash out any residual metal fluorosilicates. Separation of the remaining carbonaceous materials from the aqueous phase, and optionally washing the carbonaceous materials, affords a partially purified carbonaceous material which has a lower content of sulfur and metals compared to the original material.
  • the principal impurities typically present in the partially purified carbonaceous materials at this stage are silica and iron sulfide.
  • step (c) is typically a process in accordance with United States Patent No. 4,780,112, the disclosure of which is incorporated herein by reference.
  • step (c) is typically a process in accordance with United States Patent No. 4,780,112, the disclosure of which is incorporated herein by reference.
  • the steps of treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride may be a process as described in United States Patent No. 4,780,112.
  • the fluorine acid solution may have a composition lying between the following compositions: 4% w/w H 2 SiF 6j 92% w/w H 2 O, 4% w/w HF and 35%) w/w H 2 SiF 6 , 30%) w/w H 2 O, 35% HF.
  • the fluorine acid solution typically has a composition lying between the following compositions: 5% w/w H 2 SiF 6> 90% w/w H 2 O, 5% w/w HF and 34% w/w H 2 SiF 6 , 32% w/w H 2 O, 34% HF. More typically the composition of the fluorine acid solution is about 25% w/w H 2 SiF 6 , 50% w/w H 2 O, 25% w/w HF. This step is conveniently carried out in two stages as described in US Patent No. 4,780,112.
  • the first stage is conveniently carried out in a stirred reactor at a pressure of approximately lOOkPa and a temperature of 40-60°C
  • the second stage is conveniently carried out in a tubular reactor at a pressure within the range of about 340 to 480 kPa and a temperature of 65°C to 80°C, more usually about 70°C.
  • the temperature is maintained at this value by the exotherm of the reaction between silica present in the carbonaceous materials and hydrogen fluoride.
  • the minimum quantity of the fluorine acid solution employed is typically enough to enable the mixture of it and the carbonaceous materials to be stirred.
  • the carbonaceous materials are mixed with at least about twice their weight of the fluorine acid solution. More usually, the fluorine acid solution is present in an amount of from about 70%) to 90% by weight, relative to the total weight of the mixture, still more usually about 70% to 80% by weight of the total mixture.
  • the mixture of the carbonaceous material and the fluorine acid solution may be ultrasonically agitated as described in United States Patent No. 4,780,112, in order for any unreacted ferrous sulfide (which is relatively inert to HF and SiF 4 ) or other relatively dense impurities to be capable of being separated from the bulk of the relatively purified carbonaceous material, which is less dense than the ferrous sulfide and the aqueous phase.
  • the purified carbonaceous material may be separated from the aqueous phase, optionally washed with aqueous H SiF 6 , separated, dried to remove excess water (at about 100-110°C) and heated to a temperature within the range of about 250°C to 400°C, or 280°C to 340°C, typically about 310°C, to evaporate any residual hydrofluorosilicic acid remaining on the carbonaceous material, before being used for any desired purpose, such as for a fuel. HF and SiF 4 gases and water vapour are typically evolved during this drying step.
  • Aqueous fluorine acid separated from carbonaceous materials after it has been contacted with them is relatively enriched in SiF and depleted in HF, compared to the fluorine acid solution before it is contacted with the carbonaceous materials, as a result of the reaction:
  • the reactor in which the fluorine acid solution is contacted with the relatively purified carbonaceous materials includes a means for SiF 4 to be removed from it.
  • the spent aqueous phase from this step may be directed to a holding vessel where any excess SiF 4 is vented from it.
  • the concentration of HF in the spent aqueous phase may be increased by directing a gaseous mixture of HF and SiF 4 into the vessel, whereby the HF is absorbed and the SiF 4 passes through.
  • Vented SiF 4 is conveniently directed to a hydrolyser where it is treated with water to produce H 2 SiF 6 , and Si ⁇ 2 according to the equation
  • the silica so produced may be separated from the acid by filtration or any other convenient means.
  • the acid produced in this way is conveniently used in step (a) of the processes of the first and second embodiments.
  • aqueous streams of hydrofluorosilicic acid with or without hydrofluoric acid present, that are generated in processing steps associated with the processes of the present invention may be directed to an acid still in which the streams are combined and distilled.
  • a gaseous mixture of water, HF and SiF 4 is distilled from the still, these substances being more volatile than the 32% w/w aqueous hydrofluorosilicic acid azeotrope.
  • the gaseous mixture of water, HF and SiF 4 can be directed first to a dehydrating system for removal of water and then the resultant dehydrated gaseous mixture of the HF and SiF 4 may be separated by directing it to a holding vessel which contains a solution of H 2 SiF 6 that is saturated with respect to SiF 4 , as described above.
  • the dehydration step for a gaseous mixture of water, HF and SiF comprises contacting the gases with a sufficient quantity of anhydrous metal fluoride such as A1F 3 to absorb all the water present.
  • anhydrous metal fluoride such as A1F 3
  • Other metal fluorides that can be used include zinc fluoride and ferrous fluoride.
  • Substantially anhydrous gases may be obtained in this way, together with a hydrated metal fluoride, which may be separated from the anhydrous gases and heated to regenerate substantially anhydrous metal fluoride for recycling to the dehydration step.
  • reaction products separated from carbonaceous materials in step (b) consist of sulfur dioxide and metal fluorosilicates dissolved or suspended in aqueous H 2 SiF 6 .
  • Gaseous HC1, derived from inorganic or organic chloride in the carbonaceous material, may also be present.
  • these reaction products are directed to a still where they are heated so as to cause gaseous HF, SiF , steam, HC1 and sulfur dioxide to be evolved, and so as to cause any metal fluorosilicates present to be concentrated above their solubility limit and to separate as solids, which can be removed from the still for disposal or re-processing.
  • the gaseous mixture leaving this still may suitably be dehydrated by a process as described above, by contacting it with anhydrous alumim ' um fluoride, and subsequently passed to an activated carbon filter for removal of sulfur oxides and HC1.
  • the remaining HF and SiF 4 gases, dried and freed of sulfur dioxide, may be directed to the holding vessel for spent aqueous phase from step (c) of a process of the second embodiment, for absorption of the HF.
  • the process of the third embodiment the process may further comprise after the separating: washing the carbonaceous materials to remove any residual acid; and optionally drying the carbonaceous materials prior to the contacting.
  • the washing may be with water.
  • the drying may take place at a temperature within the range 100-120°C, typically at 110°C.
  • the organic solvent capable of dissolving elemental sulfur is typically ethanol, benzene, carbon disulfide, either or carbon tetrachlori.de, or a mixture of two or more of these or other suitable solvent capable of dissolving elemental sulfur.
  • the solvent is ethanol.
  • the step of contacting the carbonaceous materials with the organic solvent is typically carried out at ambient temperature and atmospheric pressure, but elevated temperatures (e.g. in the range of 30 - 90°C or elevated pressures (e.g. in the range of 1.01 -5 atm or 1.2-2.5 am ), or both, may also be used.
  • the quantity of solvent used is not critical, but a mimmum quantity for practical purposes is a quantity sufficient to enable the mixture to be stirred or agitated.
  • the organic solvent is contacted with the carbonaceous materials for sufficient time for at least some of the elemental sulfur, which will be present in it after the step of treating the carbonaceous material with the fluorine acid solution, to be dissolved.
  • the solvent is separated from the carbonaceous materials after this time, and is distilled to recover as much as possible for reuse.
  • the treated carbonaceous materials may also be treated to remove any residual solvent, although if the solvent includes no halogen or sulfur atoms, this step can be omitted. Removal of the residual solvent can be by any convenient means such as air blowing or heating (eg at a temperature within the range of 30-100°C the temperature chosen being dependent on the solvent).
  • the step of separating in the embodiments of the invention may comprise filtering, separating by centrifuging or other suitable separating means.
  • processes of the present invention provide several advantages over prior art processes.
  • processes of the present invention can also result in removal or partial removal of other undesirable substances in carbonaceous materials such as silica, metal oxides and metal sulfides, metals such as mercury and radioactive elements, and inorganic chlorides.
  • carbonaceous materials such as silica, metal oxides and metal sulfides, metals such as mercury and radioactive elements, and inorganic chlorides.
  • coal contained sulphur at about 8wt% it may be possible to remove this sulphur to a lower level (e.g.
  • processes of the present invention can lower the levels of bound oxygen in the carbonaceous materials and, when applied to coal, can result in an increase in its calorific value, typically by 3-4%.
  • the carbonaceous materials may reduced prior to the treating step to granular form which is less than about 4, 3, 2, 1.75, 1.5, 1.25, 1 or 0.75 mm in particle size. At least 80wt%, 85wt%, 90wt%, or 95wt% of the granular particles may be in the range of 5-0.25 mm, 4-0.25 mm, 3-0.25 mm, 2-0.25 mm, or 1-0.25 mm, for example.
  • the carbonaceous material may be treated in its raw form. If the carbonaceous material contains excess moisture it may be dried (e.g. at 60-120°C or 100-120°C) prior to processing so as to remove excess moisture.
  • the drying may be conducted for long enough so as to result in an inherent moisture content of carbonaceous material in the range 3 to 8% w/w, more usually 3 to 5% w/w, for example.
  • Some coals such as lignite which have a high water content usually have to be predried prior to processing.
  • the carbonaceous material may be air dried (e.g. at 60-120°C or 100-120°C) prior to processing by passing hot air over the carbonaceous material, for example. The temperature of the hot air used for drying the carbonaceous material is lower than that which would cause the carbonaceous material to combust.
  • Figure 1 is a schematic block diagram of a system for purification and combustion of carbonaceous material, incorporating a process in accordance with the present invention.
  • Figure 2 is a schematic block diagram of a still and associated plant for processing an aqueous solution or suspension produced by step (a) of a process of the first or second embodiments of the invention.
  • Figure 3 is a schematic block diagram of a system for the treatment of carbonaceous materials with a solvent for removal of elemental sulfur, as part of a process of the third embodiment of the invention.
  • FIG. 1 illustrates in schematic block diagram form a system 10 for purification and combustion of carbonaceous materials, incorporating a process in accordance with the present invention.
  • system 10 includes hopper 20 for holding impure carbonaceous materials which have been reduced to granular form, preferably substantially spherical particles and preferably less than about 2mm in particle size.
  • feed unit 25 for conveying carbonaceous materials from hopper 20 to purification reactor 30.
  • Purification reactor 30 is positioned to receive carbonaceous materials from feed unit 25.
  • Purification reactor 30 is also equipped with line 24 to admit an aqueous solution of approximately 32%w/w H 2 SiF 6 from a hydrolyser 32.
  • Purification reactor 30 may be a flow through reactor or a stirred or rotating reactor.
  • purification reactor 30 is a rotating drum reactor. It is also equipped with line 26 for transfer of the contents of reactor 30, after the carbonaceous material has been in contact with the aqueous H 2 SiF 6 for a suitable time, to filter 50.
  • Filter 50 is suitably a belt filter and is equipped with line 51 to conduct separated liquids away from filter 50, and conveyor 52 whereby separated solids from filter 50 are transferred to silica removal reactor 55.
  • Reactor 55 is equipped with line 58 for admitting an aqueous fluorine acid solution of HF and H SiF 6 from HF absorber 54, and vent line 59 which communicates with hydrolyser 32.
  • a bottom outlet of reactor 55 communicates via pump 56 and line 57 with a two- stage tubular reactor 65 A, 65B, the first stage 65 A of which is capable of being agitated ultrasonically.
  • the distal end of reactor 65B discharges into separator 16 which is equipped with takeoffs 66 and 67 adjacent its upper and lower ends respectively.
  • Upper takeoff 66 communicates with centrifuge or belt filter 70 which is capable of separating solid carbonaceous material from aqueous solution.
  • the liquid removal side of centrifuge or belt filter 70 is equipped with line 69 that leads to HF absorber 54, and the solids removal side of centrifuge or belt filter 70 discharges to a system of mixers and separators for washing.
  • the mixer/separator system consists of three mixing tanks 71, 73 and 75 and three separators, such as centrifuges or belt filters, 72, 74 and 76 arranged so that carbonaceous materials can flow sequentially from mixing tank 71 to separator 72, then to mixing tank 73 followed by separator 74, then to mixing tank 75 and separator 76.
  • the system is arranged so that aqueous phase moves essentially counterflow to the solids.
  • the solids exit of final separator 76 is connected to a drying system which consists of mixing vessel 77, tubular reactor 78 and solids separator 79.
  • the liquid exit of the mixer/separator system is from separator 72 and communicates with a still 80.
  • Separator 79 has a vapour off-take that also communicates with still 80, which is equipped with a jacket heater, vapour outlet 81 and a bottom outlet leading to solids separator 98.
  • a solvent extraction system such as described below with reference to
  • Figure 3 may be installed between the solids exit of separator 76 and mixing vessel 77, as shown in phantom in Figure 1.
  • Vapour outlet 81 of still 80 is connected via pressure fan 82 and mixer 83 to gas dehydration reactor 84.
  • Mixer 83 is also equipped with a connection (not shown) whereby hot gases can be admitted to it.
  • Downstream of dehydration reactor 84 is separator 86 with anhydrous gas takeoff 87 which is connected to HF absorber 54. Separator 86 is also connected to solids transfer line 88 which communicates with fluoride drier 89.
  • Fluoride drier 89 is equipped with water removal lines 91a, 91b and fluoride supply line 90 for transferring substantially anhydrous metal fluoride(s) from drier 89 to mixer 83.
  • carbonaceous material from hopper 20 is transfe ⁇ ed via feed unit 25 to reactor 30.
  • the transfer of carbonaceous material via feed unit 25 is by a system of a plurality of disks within a tube or pipe, the disks being approximately the internal diameter of the tube or pipe and connected by a cable whereby they can be drawn through the tube or pipe.
  • a suitable system is marketed under the name
  • reactor 30 is supplied to reactor 30 aqueous H 2 SiF 6 , from hydrolyser 32 via line 24.
  • Reactor 30 is typically at a temperature of about 30°C and atmospheric pressure.
  • Carbonaceous material is contacted with the aqueous H 2 SiF 6 in reactor 30 for a time sufficient for at least some of any sulfur-containing impurities in the carbonaceous material to react and dissolve.
  • This may be achieved in a flow-through reactor by controlling the flow rate of the reactant aqueous solution to provide a sufficient residence time in reactor 30.
  • the process may be carried out batchwise, with sufficient time being allowed for reaction of each batch.
  • a suitable reaction time is in the range of 10 to 100 minutes, more typically 15 to 30 minutes, still more typically 12 to 16 minutes.
  • the mixture of aqueous acid and carbonaceous materials from reactor 30 is transferred via line 26 to filter 50 in which the aqueous phase containing aqueous hydrofluorosilicic acid and dissolved metal fluorosilicates, and the like, is separated from partially purified carbonaceous materials.
  • the aqueous phase is transferred by a line 51 to still 110 (not shown in Figure 1) for separation of metal fluorides as described in more detail below with reference to Figure 2.
  • Partially purified carbonaceous material is transferred via conveyer 52 to reactor 55 where it is mixed with an aqueous fluorine acid solution comprising aqueous hydrofluorosilicic acid and hydrogen fluoride so that partially purified carbonaceous materials from purification reactor 30 can remain in contact with the aqueous fluorine acid solution for a sufficient time for at least some of any silica in the partially purified carbonaceous material to be dissolved.
  • Reactor 55 is typically maintained at a pressure in the range of about 100-135 kPa and a temperature of about 70°C. Residence time of the carbonaceous material in reactor 55 is typically from 10 to 20 minutes, more typically about 15 minutes.
  • first stage tubular reactor 65A the mixture of the carbonaceous material and aqueous fluorine acid solution is passed via pump 56 to first stage tubular reactor 65A and thence to second stage 65B.
  • the temperature in tubular reactor 65A, 65B is typically about 70°C and the pressure is typically from 350 to 500 kPa.
  • first stage reactor 65 A the suspension of carbonaceous material in aqueous acid is agitated sufficiently for any FeS and other relatively dense material present to be separable at separator 16 at the end of second stage reactor 65B.
  • second stage tubular reactor 65B the mixture is not ultrasonically agitated. From a lower portion of separator 16 a slurry of solids which are rich in FeS is removed via line 67.
  • a slurry of carbonaceous material in aqueous hydrofluorosilicic acid is removed from an upper portion of separator 16 via line 66 and transferred to centrifuge or belt filter 70 where aqueous acid is removed, leaving a carbonaceous material stream to be transferred to the washer/separator system.
  • carbonaceous material is washed with aqueous hydrofluorosilicic acid which flows through the system in the opposite direction to the direction of flow of the carbonaceous materials. That is, the fresh supply of aqueous hydrofluorosilicic acid is supplied from hydrolyser 32 to mixing tank 75 where it mixes with carbonaceous material and is separated in separator 76.
  • separator 76 From separator 76 the aqueous phase is transferred to mixing tank 73 where it is mixed with carbonaceous material entering that mixing tank, and separated therefrom in separator 74.
  • the aqueous phase separated in separator 74 is transferred to mixing tank 71 where it is mixed with carbonaceous material leaving centrifuge or belt filter 70.
  • the solids and liquids in mixing tank 71 are separated in separator 72, the solids being transferred to mixing tank 73 and the liquids being transferred to still 80. Solids leaving separator 76 are thus washed solids, and liquid leaving separator 72 is relatively impure.
  • Carbonaceous material leaving the final separator 76 in the sequence of vessels is admitted (optionally via a solvent extraction system) to a drying system which consists of mixing vessel 77 and steel tube reactor 78.
  • the carbonaceous material entering mixing vessel 77 is mixed with oxygen-depleted combustion gases and transferred to reactor 78 where it is baked under inert atmosphere, typically at about 310°C, to remove the remaining hydrofluorosilicic acid from the surface of the carbonaceous material.
  • the hydrofluorosilicic acid is removed as gaseous hydrogen fluoride and silicon tetrafluoride, together with steam, which gases are directed to still 80 after the gases and the dried solids are separated in separator 79.
  • Dried solids exiting separator 79 are purified carbonaceous materials which are suitable for use as a combustible fuel.
  • System 10 further includes carbonaceous materials storage container 93 from which dried carbonaceous material can be supplied to furnace and gas turbine system 95.
  • system 10 includes a solvent extraction stage as described below with reference to Figure
  • Aqueous phase removed from centrifuge or belt filter 70 is passed to HF absorber 54 where gases from drier 84 and separator 86 are admitted for absorption of HF to generate the fluorine acid solution to be supplied to silica removal reactor 55. Also supplied to HF absorber 54, via line 53, and HF and SiF 4 gases from system 100 as illustrated in Figure 2 and described in more detail below. Gases leaving HF absorber 54 pass to hydrolyser 32 to which water 36 is added in sufficient amount to produce aqueous H 2 SiF 6 of the desired concentration for use in reactor 30. Silica generated in hydrolyser 32 is removed via a bottom outlet.
  • Aqueous acid leaving the washer/separator system at separator 72 is transferred to still 80 where it is heated to sufficient temperature (typically 105 to 110 °C) to cause hydrogen fluoride and silicon tetrafluoride gases to be liberated from the aqueous solution and any metal fluorides that had been contained in the aqueous phase to separate out as solids. It will be appreciated that the pressure difference across fan 82 will affect the pressure in still 80 and hence its temperature. The separated solids are removed from still 80 via separator 98. Still 80 is typically heated by exhaust gas from gas turbine 85. Vapours from mixing vessel 77 and separator 79 are typically returned to still 80 and provide a further source of heat.
  • sufficient temperature typically 105 to 110 °C
  • Gases leaving still 80 are passed via line 81 and pressure fan 82 to mixer 83 in which they are mixed with substantially anhydrous A1F 3 .
  • the mixture is passed through tubular dehydration reactor 84 leading to removal of substantially all the water from the gaseous phase, thereby producing a substantially anhydrous gaseous mixture of HF and SiF 4 which is transferred from dehydration reactor 84 to HF absorber 54 via line 87.
  • Moist A1F 3 produced in dehydration reactor 84 is transferred to A1F 3 drier 89 in which the moist A1F 3 is heated. Water vapour generated by this heating is removed at 91a and 91b, and substantially anhydrous A1F 3 is recycled via line 90 to mixer 83.
  • FIG. 2 illustrates in schematic block diagram form a system 100 comprising a still and associated plant for processing an aqueous solution or suspension produced by step (a) of a process of the first or second embodiments of the invention.
  • system 100 includes still 110 equipped with supply line 115 communicating with filter 50 as illustrated in Figure 1.
  • Still 110 is also equipped with jacket heater 112, vapour outlet 120 and a bottom outlet connected to level controlled separator 150.
  • Gas outlet 120 communicates via pressure fan 125 to water removal system 130, the gas outlet of which is connected to a pair of activated carbon filters 135,
  • Condenser 140 is equipped with vent
  • Carbon filters 135, 136 are respectively equipped with gas outlets 138 and 139, and are connected to steam supply line 133.
  • aqueous phase leaving reactor 30 as illustrated in Figure 1 and separated from solids at filter 50 is admitted to still 110 via line 115, and still 110 is heated by jacket heater 112 to a temperature sufficient for gases comprising HF, SiF 4 , sulfur dioxide and water vapour to be evolved from still 110 and leave via outlet 120.
  • gases comprising HF, SiF 4 , sulfur dioxide and water vapour to be evolved from still 110 and leave via outlet 120.
  • gases are pressurised by fan 125, typically to a pressure in the range of about 70-140 kPa, and passed into a water removal system 130 including anhydrous aluminium fluoride, as described above with reference to Figure 1.
  • the temperature of still 110 is dependent on the pressure generated by fan 125, but is typically in the range of 105 to 110 °C.
  • water vapour is substantially removed and substantially anhydrous gases leave the water removal system and are admitted to one or the other of activated carbon filters 135, 136.
  • activated carbon filters 135, 136 As the gases pass through the activated carbon filter, sulfur dioxide and certain other gases that may be present, such as HCl, are absorbed by the activated carbon, generating a stream of gaseous HF and SiF 4 which is removed at gas outlet 138 or 139 and transferred to HF absorber 54 of system 10 as shown in Figure 1, via line 53 thereof.
  • activated carbon filters 135, 136 are used in tandem so that one of the activated carbon filters is on-stream and being contacted with gases leaving water removal system 130 while the other activated carbon filter is off-stream and is being heated to desorb sulfur dioxide and other absorbed species such as hydrogen chloride.
  • the heating is by means of steam admitted via line 133.
  • the desorbed species are transferred from the activated carbon filter which is being cleaned in this way to steam condenser 140 where the steam is condensed and removed, together with dissolved SO and any HCl present, via drain 146.
  • Liquids in still 110 become more concentrated as a result of the heating and evaporation of gases therefrom, until a point where dissolved inorganics in the liquids exceed their solubility limit.
  • Inorganic solids accumulating in still 110 can be removed from the bottom outlet of the still and passed to a level controlled separator 150 from which solids can be separated from the liquid phase by any convenient means and can be directed either to disposal or to a reprocessing plant to obtain useful materials therefrom.
  • Figure 3 illustrates in schematic form a system 200 for treatment of partially purified carbonaceous materials with a solvent capable of dissolving elemental sulfur, in accordance with a process of the third embodiment of the invention.
  • system 200 includes treatment vessel 210 which is equipped with carbonaceous material inlet 215 and solvent inlet 216, as well as outlet 218 to permit transfer of carbonaceous material and solvent from treatment vessel 210 to solid/liquid separator 220.
  • Separator 220 may be any convenient form of separator such as filter or centrifuge, or settler.
  • Separator 220 is equipped with a solids removal outlet connected to stripper 230 and a liquids outlet 225 connected to a still (not shown).
  • Stripper 230 is equipped with a heater (not shown), vapour off-take line 237 and solids outlet 235.
  • treatment vessel 210 4,780,112, and solvent are charged into treatment vessel 210 where they are mixed and allowed to remain in contact for sufficient time for at least part of any elemental sulfur present in the carbonaceous materials to be dissolved by the solvent.
  • the solvent is typically ethanol, but may be any other solvent which is capable of dissolving elemental sulfur, or a mixture of such solvents.
  • the treatment in the treatment vessel 210 is typically at ambient temperature and atmospheric pressure. After an appropriate contact time, the contents of treatment vessel 210 are conveyed via bottom outlet 218 to separator 220 in which the solids phase is separated from the solvent phase. The solids phase is transferred to stripper 230 where it is heated, causing residual solvent to evaporate. Suitably, the temperature of heating is at or about the boiling point of the solvent used.
  • Liquids leaving separator 220 and vapour leaving stripper 230 may be passed to a solvent still (not shown) in which the solvent is distilled for recovery and reuse, the other major product in the still being elemental sulfur which is removed for disposal or sale.
  • 4,780,112 were dried and examined under an electron microscope. They were observed to contain sulfur in two forms, pyrite and elemental sulfur.
  • a raw high-sulfur coal sample was treated with about twice its weight of 32% w/w aqueous hydrofluorosilicic acid for 30 minutes at ambient temperature, then dried and treated with an aqueous fluorine acid solution as described in United States Patent No. 4,780,112. After separation of the solids they were again dried and examined under the electron microscope. No elemental sulfur was visible.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Carbon And Carbon Compounds (AREA)
  • Silicon Compounds (AREA)

Abstract

Process for reducing the amount of sulfur-containing impurities in carbonaceous materials are described. One process comprises contacting the materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products and separating the reaction products from the carbonaceous materials. Another process comprises contacting the materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products, separating the reaction products and the hydrofluorosilicic acid from the carbonaceous materials and subsequently treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride. A further process comprises treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and then contacting the carbonaceous materials with an organic solvent capable of dissolving elemental sulfur.

Description

Method For Treating Carbonaceous Materials
Technical Field
The invention relates to methods for treating carbonaceous materials to remove or substantially decrease the amount of non-carbonaceous impurities therein.
Background of the Invention
United States Patent No. 4,780,112 describes a process for treating carbon to reduce the ash therein. The process involves treating the carbon with an aqueous solution of hydrofluorosilicic acid (H2SiF6) and hydrofluoric acid (HF), whereby metal oxides in the carbon are converted to metal fluorides and/or metal fluorosilicates, from which carbon is then separated. The process described in United States Patent No. 4,780,112 is effective for removal of metal oxides from carbon, but the present inventor has surprisingly discovered that when carbon that includes sulfur-containing impurities is treated by the process of United States Patent No. 4,780,112, the purified carbon is still contaminated with sulfur. The present inventor has surprisingly discovered that the remaining sulfur is present as elemental sulfur, which in some circumstances is visible when the carbon is viewed under a microscope.
The presence of sulfur in carbon that is intended to be used as a fuel is undesirable, since combustion of the carbon will lead to conversion of the sulfur into sulfur oxides. As a result, the flue gases generated by the combustion of the carbon need to be scrubbed or otherwise substantially freed of the sulfur oxides before they can be discharged into the atmosphere if release of sulfur oxides into the environment is to be avoided.
Accordingly, there is a need for an improved process for treating carbonaceous materials to decrease the amount of non-carbonaceous impurities therein, and in particular there is a need for an improved process for removing or at least substantially reducing the amount of sulfur in carbonaceous materials.
Surprisingly, the present inventor has discovered that the amount of sulfur- containing impurities in carbonaceous materials can be substantially decreased by a process which involves treating the carbonaceous materials with an aqueous solution of hydrofluorosilicic acid, or with an organic solvent capable of dissolving elemental sulfur. Summary of the Invention
According to a first embodiment of the invention there is provided a process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising (a) contacting the materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products, and (b) separating the reaction products from the carbonaceous materials.
According to a second embodiment of the invention there is provided a process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising
(a) contacting the materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of the sulfur- containing impurities react with the hydrofluorosilicic acid to form reaction products;
(b) separating the reaction products and the hydrofluorosilicic acid from the carbonaceous materials and subsequently
(c) treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride.
According to a third embodiment of the invention there is provided a process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and then contacting the carbonaceous materials with an organic solvent capable of dissolving elemental sulfur. As used herein, the term "carbonaceous materials" is to be understood to mean materials which consist predominantly of elemental carbon. Examples of carbonaceous materials include coal including brown coal, coke, lignite, anthracite, charcoal, graphite and the like.
As used herein, unless the context clearly indicates otherwise, the words "comprise", "comprises", "comprising" or other variations thereof shall be understood as meaning that the stated integer or integers is or are included but that other integers are not necessarily excluded from being present.
Detailed Description of the Invention
In the processes of the first and second embodiments of the invention, the concentration of hydrofluorosilicic acid in the step of contacting the materials with an aqueous solution of hydrofluorosilicic acid under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products may be in the range of 27% to 37% (w/v or w/w or v/w). The concentration of hydrofluorosilicic acid in the step of contacting the materials with an aqueous solution of hydrofluorosilicic acid under conditions wherein at least some of the sulfur-containing impurities react with the hydrofluorosilicic acid to form reaction products is typically in the range of 28% to 36%, more typically about 32%(w/v or w/w or v/w). The process is usually carried out at atmospheric pressure, but the pressure can also be above or below atmospheric. The temperature may be in the range 28 to 75°C. Typically, the temperature is in the range of 30 to 70 °C, more usually 30 to 40 °C. The reaction time may be in the range 8 to 120 minutes. The reaction time is typically from 10 to 100 minutes, more usually 15 to 30 minutes, still more usually 12 to 16 minutes. The minimum quantity of aqueous hydrofluorosilicic acid employed is typically enough to enable the mixture of it and the carbonaceous materials to be stirred in the acid. Usually, the carbonaceous materials are mixed with at least about twice their weight of the aqueous hydrofluorosilicic acid. More usually, the aqueous hydrofluorosilicic acid is present in an amount of from about 70% to 90% by weight, relative to the total weight of the mixture, still more usually about 70% to 80% by weight of the total weight of the mixture.
In step (a) of the processes of the first and second embodiments of the invention, many metal oxides and some metals present in the carbonaceous materials are converted, at least partially, into the corresponding metal fluorosilicates, with water being the other product. Examples of metals or metal oxides converted to their fluorosilicates are nickel, aluminium, calcium, and mercury and their oxides. Sulfur compounds present are converted, under the reaction conditions, to sulfur dioxide and/or sulfur tetrafluoride. After step (a) of the processes of the first and second embodiments of the invention, relatively purified carbonaceous materials remain mixed with an aqueous solution containing dissolved metal fluorosilicates. Suitably, this mixture of carbonaceous materials and metal fluorosilicates may be filtered or centrifuged to separate the relatively purified carbonaceous materials. Optionally, the filtered relatively purified carbonaceous materials may be treated with further aqueous hydrofluorosilicic acid, typically having a concentration of 32% by weight of hydrofluorosilicic acid, to wash out any residual metal fluorosilicates. Separation of the remaining carbonaceous materials from the aqueous phase, and optionally washing the carbonaceous materials, affords a partially purified carbonaceous material which has a lower content of sulfur and metals compared to the original material. The principal impurities typically present in the partially purified carbonaceous materials at this stage are silica and iron sulfide. The partially purified carbonaceous material may be further purified to remove other impurities that are not removed in step (a). Thus, the process of the second embodiment provides such a process. In the process of the second embodiment, step (c) is typically a process in accordance with United States Patent No. 4,780,112, the disclosure of which is incorporated herein by reference. Similarly, in the process of the third embodiment, the steps of treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and separating the carbonaceous materials from the aqueous solution of hydrofluorosilicic acid and hydrogen fluoride may be a process as described in United States Patent No. 4,780,112. i step (c) of the process of the second embodiment, and in the process of the third embodiment, the fluorine acid solution may have a composition lying between the following compositions: 4% w/w H2SiF6j 92% w/w H2O, 4% w/w HF and 35%) w/w H2SiF6, 30%) w/w H2O, 35% HF. In step (c) of the process of the second embodiment, and in the process of the third embodiment, the fluorine acid solution typically has a composition lying between the following compositions: 5% w/w H2SiF6> 90% w/w H2O, 5% w/w HF and 34% w/w H2SiF6, 32% w/w H2O, 34% HF. More typically the composition of the fluorine acid solution is about 25% w/w H2SiF6, 50% w/w H2O, 25% w/w HF. This step is conveniently carried out in two stages as described in US Patent No. 4,780,112. That is, the first stage is conveniently carried out in a stirred reactor at a pressure of approximately lOOkPa and a temperature of 40-60°C, and the second stage is conveniently carried out in a tubular reactor at a pressure within the range of about 340 to 480 kPa and a temperature of 65°C to 80°C, more usually about 70°C. Typically, the temperature is maintained at this value by the exotherm of the reaction between silica present in the carbonaceous materials and hydrogen fluoride. In step (c) the minimum quantity of the fluorine acid solution employed is typically enough to enable the mixture of it and the carbonaceous materials to be stirred. Usually, the carbonaceous materials are mixed with at least about twice their weight of the fluorine acid solution. More usually, the fluorine acid solution is present in an amount of from about 70%) to 90% by weight, relative to the total weight of the mixture, still more usually about 70% to 80% by weight of the total mixture.
Suitably, in step (c) of the process of the second embodiment, and in the process of the third embodiment, after being mixed with aqueous hydrofluorosilicic acid and hydrogen fluoride, the mixture of the carbonaceous material and the fluorine acid solution may be ultrasonically agitated as described in United States Patent No. 4,780,112, in order for any unreacted ferrous sulfide (which is relatively inert to HF and SiF4) or other relatively dense impurities to be capable of being separated from the bulk of the relatively purified carbonaceous material, which is less dense than the ferrous sulfide and the aqueous phase. The purified carbonaceous material may be separated from the aqueous phase, optionally washed with aqueous H SiF6, separated, dried to remove excess water (at about 100-110°C) and heated to a temperature within the range of about 250°C to 400°C, or 280°C to 340°C, typically about 310°C, to evaporate any residual hydrofluorosilicic acid remaining on the carbonaceous material, before being used for any desired purpose, such as for a fuel. HF and SiF4 gases and water vapour are typically evolved during this drying step.
Aqueous fluorine acid separated from carbonaceous materials after it has been contacted with them is relatively enriched in SiF and depleted in HF, compared to the fluorine acid solution before it is contacted with the carbonaceous materials, as a result of the reaction:
SiO2 + 4HF -> SiF4 + 2H2O.
This spent aqueous phase, if is recycled to the step of being contacted with the relatively purified carbonaceous material, thus tends to reach a point where it becomes saturated with respect to SiF4, at which point any further SiF4 generated as a result of further reaction is evolved as a gas. Conveniently, the reactor in which the fluorine acid solution is contacted with the relatively purified carbonaceous materials includes a means for SiF4 to be removed from it. Suitably, the spent aqueous phase from this step may be directed to a holding vessel where any excess SiF4 is vented from it. The concentration of HF in the spent aqueous phase may be increased by directing a gaseous mixture of HF and SiF4 into the vessel, whereby the HF is absorbed and the SiF4 passes through. Vented SiF4 is conveniently directed to a hydrolyser where it is treated with water to produce H2SiF6, and Siθ2 according to the equation
3SiF4 + 2H2O → 2H2SiF6 + SiO2
The silica so produced may be separated from the acid by filtration or any other convenient means. The acid produced in this way is conveniently used in step (a) of the processes of the first and second embodiments. Advantageously, aqueous streams of hydrofluorosilicic acid with or without hydrofluoric acid present, that are generated in processing steps associated with the processes of the present invention, may be directed to an acid still in which the streams are combined and distilled. A gaseous mixture of water, HF and SiF4 is distilled from the still, these substances being more volatile than the 32% w/w aqueous hydrofluorosilicic acid azeotrope. The gaseous mixture of water, HF and SiF4 can be directed first to a dehydrating system for removal of water and then the resultant dehydrated gaseous mixture of the HF and SiF4 may be separated by directing it to a holding vessel which contains a solution of H2SiF6 that is saturated with respect to SiF4, as described above.
Suitably, the dehydration step for a gaseous mixture of water, HF and SiF comprises contacting the gases with a sufficient quantity of anhydrous metal fluoride such as A1F3 to absorb all the water present. Other metal fluorides that can be used include zinc fluoride and ferrous fluoride. Substantially anhydrous gases may be obtained in this way, together with a hydrated metal fluoride, which may be separated from the anhydrous gases and heated to regenerate substantially anhydrous metal fluoride for recycling to the dehydration step.
In one form of the processes of the first and second embodiments, reaction products separated from carbonaceous materials in step (b) consist of sulfur dioxide and metal fluorosilicates dissolved or suspended in aqueous H2SiF6. Gaseous HC1, derived from inorganic or organic chloride in the carbonaceous material, may also be present. Suitably, these reaction products are directed to a still where they are heated so as to cause gaseous HF, SiF , steam, HC1 and sulfur dioxide to be evolved, and so as to cause any metal fluorosilicates present to be concentrated above their solubility limit and to separate as solids, which can be removed from the still for disposal or re-processing. The gaseous mixture leaving this still may suitably be dehydrated by a process as described above, by contacting it with anhydrous alumim'um fluoride, and subsequently passed to an activated carbon filter for removal of sulfur oxides and HC1. The remaining HF and SiF4 gases, dried and freed of sulfur dioxide, may be directed to the holding vessel for spent aqueous phase from step (c) of a process of the second embodiment, for absorption of the HF. the process of the third embodiment the process may further comprise after the separating: washing the carbonaceous materials to remove any residual acid; and optionally drying the carbonaceous materials prior to the contacting.
The washing may be with water. The drying may take place at a temperature within the range 100-120°C, typically at 110°C.
In a process of the third embodiment, the organic solvent capable of dissolving elemental sulfur is typically ethanol, benzene, carbon disulfide, either or carbon tetrachlori.de, or a mixture of two or more of these or other suitable solvent capable of dissolving elemental sulfur. Typically, the solvent is ethanol. The step of contacting the carbonaceous materials with the organic solvent is typically carried out at ambient temperature and atmospheric pressure, but elevated temperatures (e.g. in the range of 30 - 90°C or elevated pressures (e.g. in the range of 1.01 -5 atm or 1.2-2.5 am ), or both, may also be used. The quantity of solvent used is not critical, but a mimmum quantity for practical purposes is a quantity sufficient to enable the mixture to be stirred or agitated.
Suitably, in the process of the third embodiment the organic solvent is contacted with the carbonaceous materials for sufficient time for at least some of the elemental sulfur, which will be present in it after the step of treating the carbonaceous material with the fluorine acid solution, to be dissolved. Conveniently, the solvent is separated from the carbonaceous materials after this time, and is distilled to recover as much as possible for reuse. The treated carbonaceous materials may also be treated to remove any residual solvent, although if the solvent includes no halogen or sulfur atoms, this step can be omitted. Removal of the residual solvent can be by any convenient means such as air blowing or heating (eg at a temperature within the range of 30-100°C the temperature chosen being dependent on the solvent). The step of separating in the embodiments of the invention may comprise filtering, separating by centrifuging or other suitable separating means.
The processes of the present invention provide several advantages over prior art processes. In addition to providing carbonaceous materials that have significantly lower levels of sulfur than treated carbonaceous materials obtainable by the process of United States Patent No. 4,780,112, processes of the present invention can also result in removal or partial removal of other undesirable substances in carbonaceous materials such as silica, metal oxides and metal sulfides, metals such as mercury and radioactive elements, and inorganic chlorides. For example, if coal contained sulphur at about 8wt% it may be possible to remove this sulphur to a lower level (e.g. about or less than 2wt% or about or less than 1 wt% or about or less than 0.5wt%) by subjecting the coal to one (or more) cycles of the processes of the first to third embodiments. Removal of inorganic chlorides, mercury and radioactive elements, in particular, is more effective with a process of the second embodiment, than with the process of United States Patent No. 4,780,112. Further, processes of the present invention can lower the levels of bound oxygen in the carbonaceous materials and, when applied to coal, can result in an increase in its calorific value, typically by 3-4%.
In the first to third embodiments the carbonaceous materials may reduced prior to the treating step to granular form which is less than about 4, 3, 2, 1.75, 1.5, 1.25, 1 or 0.75 mm in particle size. At least 80wt%, 85wt%, 90wt%, or 95wt% of the granular particles may be in the range of 5-0.25 mm, 4-0.25 mm, 3-0.25 mm, 2-0.25 mm, or 1-0.25 mm, for example. Alternatively, the carbonaceous material may be treated in its raw form. If the carbonaceous material contains excess moisture it may be dried (e.g. at 60-120°C or 100-120°C) prior to processing so as to remove excess moisture. The drying may be conducted for long enough so as to result in an inherent moisture content of carbonaceous material in the range 3 to 8% w/w, more usually 3 to 5% w/w, for example. Some coals such as lignite which have a high water content usually have to be predried prior to processing. The carbonaceous material may be air dried (e.g. at 60-120°C or 100-120°C) prior to processing by passing hot air over the carbonaceous material, for example. The temperature of the hot air used for drying the carbonaceous material is lower than that which would cause the carbonaceous material to combust. Brief Description of the Drawings
Figure 1 is a schematic block diagram of a system for purification and combustion of carbonaceous material, incorporating a process in accordance with the present invention. Figure 2 is a schematic block diagram of a still and associated plant for processing an aqueous solution or suspension produced by step (a) of a process of the first or second embodiments of the invention.
Figure 3 is a schematic block diagram of a system for the treatment of carbonaceous materials with a solvent for removal of elemental sulfur, as part of a process of the third embodiment of the invention.
Best Method of Carrying out the Invention
Figure 1 illustrates in schematic block diagram form a system 10 for purification and combustion of carbonaceous materials, incorporating a process in accordance with the present invention. Referring to Figure 1, system 10 includes hopper 20 for holding impure carbonaceous materials which have been reduced to granular form, preferably substantially spherical particles and preferably less than about 2mm in particle size. Associated with hopper 20 is feed unit 25 for conveying carbonaceous materials from hopper 20 to purification reactor 30. Purification reactor 30 is positioned to receive carbonaceous materials from feed unit 25. Purification reactor 30 is also equipped with line 24 to admit an aqueous solution of approximately 32%w/w H2SiF6 from a hydrolyser 32. Purification reactor 30 may be a flow through reactor or a stirred or rotating reactor. Typically, purification reactor 30 is a rotating drum reactor. It is also equipped with line 26 for transfer of the contents of reactor 30, after the carbonaceous material has been in contact with the aqueous H2SiF6 for a suitable time, to filter 50. Filter 50 is suitably a belt filter and is equipped with line 51 to conduct separated liquids away from filter 50, and conveyor 52 whereby separated solids from filter 50 are transferred to silica removal reactor 55. Reactor 55 is equipped with line 58 for admitting an aqueous fluorine acid solution of HF and H SiF6 from HF absorber 54, and vent line 59 which communicates with hydrolyser 32. A bottom outlet of reactor 55 communicates via pump 56 and line 57 with a two- stage tubular reactor 65 A, 65B, the first stage 65 A of which is capable of being agitated ultrasonically. The distal end of reactor 65B discharges into separator 16 which is equipped with takeoffs 66 and 67 adjacent its upper and lower ends respectively. Upper takeoff 66 communicates with centrifuge or belt filter 70 which is capable of separating solid carbonaceous material from aqueous solution. The liquid removal side of centrifuge or belt filter 70 is equipped with line 69 that leads to HF absorber 54, and the solids removal side of centrifuge or belt filter 70 discharges to a system of mixers and separators for washing. The mixer/separator system consists of three mixing tanks 71, 73 and 75 and three separators, such as centrifuges or belt filters, 72, 74 and 76 arranged so that carbonaceous materials can flow sequentially from mixing tank 71 to separator 72, then to mixing tank 73 followed by separator 74, then to mixing tank 75 and separator 76. The system is arranged so that aqueous phase moves essentially counterflow to the solids. The solids exit of final separator 76 is connected to a drying system which consists of mixing vessel 77, tubular reactor 78 and solids separator 79. The liquid exit of the mixer/separator system is from separator 72 and communicates with a still 80. Separator 79 has a vapour off-take that also communicates with still 80, which is equipped with a jacket heater, vapour outlet 81 and a bottom outlet leading to solids separator 98. Optionally, a solvent extraction system such as described below with reference to
Figure 3 may be installed between the solids exit of separator 76 and mixing vessel 77, as shown in phantom in Figure 1.
Vapour outlet 81 of still 80 is connected via pressure fan 82 and mixer 83 to gas dehydration reactor 84. Mixer 83 is also equipped with a connection (not shown) whereby hot gases can be admitted to it. Downstream of dehydration reactor 84 is separator 86 with anhydrous gas takeoff 87 which is connected to HF absorber 54. Separator 86 is also connected to solids transfer line 88 which communicates with fluoride drier 89. Fluoride drier 89 is equipped with water removal lines 91a, 91b and fluoride supply line 90 for transferring substantially anhydrous metal fluoride(s) from drier 89 to mixer 83.
When system 10 is in use, carbonaceous material from hopper 20 is transfeπed via feed unit 25 to reactor 30. Suitably, the transfer of carbonaceous material via feed unit 25 is by a system of a plurality of disks within a tube or pipe, the disks being approximately the internal diameter of the tube or pipe and connected by a cable whereby they can be drawn through the tube or pipe. A suitable system is marketed under the name
"Floveyer" by GPM Australia Pty Ltd of Leichardt, New South Wales. The transfer of material may be continuous or batchwise. Also supplied to reactor 30 is aqueous H2SiF6, from hydrolyser 32 via line 24. Reactor 30 is typically at a temperature of about 30°C and atmospheric pressure.
Carbonaceous material is contacted with the aqueous H2SiF6 in reactor 30 for a time sufficient for at least some of any sulfur-containing impurities in the carbonaceous material to react and dissolve. This may be achieved in a flow-through reactor by controlling the flow rate of the reactant aqueous solution to provide a sufficient residence time in reactor 30. Alternatively, the process may be carried out batchwise, with sufficient time being allowed for reaction of each batch. Typically a suitable reaction time is in the range of 10 to 100 minutes, more typically 15 to 30 minutes, still more typically 12 to 16 minutes.
The mixture of aqueous acid and carbonaceous materials from reactor 30 is transferred via line 26 to filter 50 in which the aqueous phase containing aqueous hydrofluorosilicic acid and dissolved metal fluorosilicates, and the like, is separated from partially purified carbonaceous materials. The aqueous phase is transferred by a line 51 to still 110 (not shown in Figure 1) for separation of metal fluorides as described in more detail below with reference to Figure 2.
Partially purified carbonaceous material is transferred via conveyer 52 to reactor 55 where it is mixed with an aqueous fluorine acid solution comprising aqueous hydrofluorosilicic acid and hydrogen fluoride so that partially purified carbonaceous materials from purification reactor 30 can remain in contact with the aqueous fluorine acid solution for a sufficient time for at least some of any silica in the partially purified carbonaceous material to be dissolved. Reactor 55 is typically maintained at a pressure in the range of about 100-135 kPa and a temperature of about 70°C. Residence time of the carbonaceous material in reactor 55 is typically from 10 to 20 minutes, more typically about 15 minutes.
From reactor 55 the mixture of the carbonaceous material and aqueous fluorine acid solution is passed via pump 56 to first stage tubular reactor 65A and thence to second stage 65B. The temperature in tubular reactor 65A, 65B is typically about 70°C and the pressure is typically from 350 to 500 kPa. In first stage reactor 65 A the suspension of carbonaceous material in aqueous acid is agitated sufficiently for any FeS and other relatively dense material present to be separable at separator 16 at the end of second stage reactor 65B. In second stage tubular reactor 65B, the mixture is not ultrasonically agitated. From a lower portion of separator 16 a slurry of solids which are rich in FeS is removed via line 67. A slurry of carbonaceous material in aqueous hydrofluorosilicic acid is removed from an upper portion of separator 16 via line 66 and transferred to centrifuge or belt filter 70 where aqueous acid is removed, leaving a carbonaceous material stream to be transferred to the washer/separator system. hi this system, carbonaceous material is washed with aqueous hydrofluorosilicic acid which flows through the system in the opposite direction to the direction of flow of the carbonaceous materials. That is, the fresh supply of aqueous hydrofluorosilicic acid is supplied from hydrolyser 32 to mixing tank 75 where it mixes with carbonaceous material and is separated in separator 76. From separator 76 the aqueous phase is transferred to mixing tank 73 where it is mixed with carbonaceous material entering that mixing tank, and separated therefrom in separator 74. The aqueous phase separated in separator 74 is transferred to mixing tank 71 where it is mixed with carbonaceous material leaving centrifuge or belt filter 70. The solids and liquids in mixing tank 71 are separated in separator 72, the solids being transferred to mixing tank 73 and the liquids being transferred to still 80. Solids leaving separator 76 are thus washed solids, and liquid leaving separator 72 is relatively impure.
Carbonaceous material leaving the final separator 76 in the sequence of vessels is admitted (optionally via a solvent extraction system) to a drying system which consists of mixing vessel 77 and steel tube reactor 78. The carbonaceous material entering mixing vessel 77 is mixed with oxygen-depleted combustion gases and transferred to reactor 78 where it is baked under inert atmosphere, typically at about 310°C, to remove the remaining hydrofluorosilicic acid from the surface of the carbonaceous material. The hydrofluorosilicic acid is removed as gaseous hydrogen fluoride and silicon tetrafluoride, together with steam, which gases are directed to still 80 after the gases and the dried solids are separated in separator 79. Dried solids exiting separator 79 are purified carbonaceous materials which are suitable for use as a combustible fuel. System 10 further includes carbonaceous materials storage container 93 from which dried carbonaceous material can be supplied to furnace and gas turbine system 95. Optionally, system 10 includes a solvent extraction stage as described below with reference to Figure
3, between separator 79 and storage container 93 as illustrated in phantom in Figure 1.
Aqueous phase removed from centrifuge or belt filter 70 is passed to HF absorber 54 where gases from drier 84 and separator 86 are admitted for absorption of HF to generate the fluorine acid solution to be supplied to silica removal reactor 55. Also supplied to HF absorber 54, via line 53, and HF and SiF4 gases from system 100 as illustrated in Figure 2 and described in more detail below. Gases leaving HF absorber 54 pass to hydrolyser 32 to which water 36 is added in sufficient amount to produce aqueous H2SiF6 of the desired concentration for use in reactor 30. Silica generated in hydrolyser 32 is removed via a bottom outlet.
Aqueous acid leaving the washer/separator system at separator 72 is transferred to still 80 where it is heated to sufficient temperature (typically 105 to 110 °C) to cause hydrogen fluoride and silicon tetrafluoride gases to be liberated from the aqueous solution and any metal fluorides that had been contained in the aqueous phase to separate out as solids. It will be appreciated that the pressure difference across fan 82 will affect the pressure in still 80 and hence its temperature. The separated solids are removed from still 80 via separator 98. Still 80 is typically heated by exhaust gas from gas turbine 85. Vapours from mixing vessel 77 and separator 79 are typically returned to still 80 and provide a further source of heat.
Gases leaving still 80 are passed via line 81 and pressure fan 82 to mixer 83 in which they are mixed with substantially anhydrous A1F3. The mixture is passed through tubular dehydration reactor 84 leading to removal of substantially all the water from the gaseous phase, thereby producing a substantially anhydrous gaseous mixture of HF and SiF4 which is transferred from dehydration reactor 84 to HF absorber 54 via line 87. Moist A1F3 produced in dehydration reactor 84 is transferred to A1F3 drier 89 in which the moist A1F3 is heated. Water vapour generated by this heating is removed at 91a and 91b, and substantially anhydrous A1F3 is recycled via line 90 to mixer 83. Exhaust gases from gas turbine 95 are conveniently used for the purpose of heating drier 89. Figure 2 illustrates in schematic block diagram form a system 100 comprising a still and associated plant for processing an aqueous solution or suspension produced by step (a) of a process of the first or second embodiments of the invention. Referring to Figure 2, system 100 includes still 110 equipped with supply line 115 communicating with filter 50 as illustrated in Figure 1. Still 110 is also equipped with jacket heater 112, vapour outlet 120 and a bottom outlet connected to level controlled separator 150. Gas outlet 120 communicates via pressure fan 125 to water removal system 130, the gas outlet of which is connected to a pair of activated carbon filters 135,
136 which are connected to steam condenser 140. Condenser 140 is equipped with vent
145 and drain 146. Carbon filters 135, 136 are respectively equipped with gas outlets 138 and 139, and are connected to steam supply line 133.
In use, aqueous phase leaving reactor 30 as illustrated in Figure 1 and separated from solids at filter 50 is admitted to still 110 via line 115, and still 110 is heated by jacket heater 112 to a temperature sufficient for gases comprising HF, SiF4, sulfur dioxide and water vapour to be evolved from still 110 and leave via outlet 120. These gases are pressurised by fan 125, typically to a pressure in the range of about 70-140 kPa, and passed into a water removal system 130 including anhydrous aluminium fluoride, as described above with reference to Figure 1. The temperature of still 110 is dependent on the pressure generated by fan 125, but is typically in the range of 105 to 110 °C. In water removal system 130, water vapour is substantially removed and substantially anhydrous gases leave the water removal system and are admitted to one or the other of activated carbon filters 135, 136. As the gases pass through the activated carbon filter, sulfur dioxide and certain other gases that may be present, such as HCl, are absorbed by the activated carbon, generating a stream of gaseous HF and SiF4 which is removed at gas outlet 138 or 139 and transferred to HF absorber 54 of system 10 as shown in Figure 1, via line 53 thereof. Conveniently, activated carbon filters 135, 136 are used in tandem so that one of the activated carbon filters is on-stream and being contacted with gases leaving water removal system 130 while the other activated carbon filter is off-stream and is being heated to desorb sulfur dioxide and other absorbed species such as hydrogen chloride. The heating is by means of steam admitted via line 133. The desorbed species are transferred from the activated carbon filter which is being cleaned in this way to steam condenser 140 where the steam is condensed and removed, together with dissolved SO and any HCl present, via drain 146.
Liquids in still 110 become more concentrated as a result of the heating and evaporation of gases therefrom, until a point where dissolved inorganics in the liquids exceed their solubility limit. Inorganic solids accumulating in still 110 can be removed from the bottom outlet of the still and passed to a level controlled separator 150 from which solids can be separated from the liquid phase by any convenient means and can be directed either to disposal or to a reprocessing plant to obtain useful materials therefrom.
The separated liquids can be returned to still 110. Figure 3 illustrates in schematic form a system 200 for treatment of partially purified carbonaceous materials with a solvent capable of dissolving elemental sulfur, in accordance with a process of the third embodiment of the invention.
Referring to Figure 3, system 200 includes treatment vessel 210 which is equipped with carbonaceous material inlet 215 and solvent inlet 216, as well as outlet 218 to permit transfer of carbonaceous material and solvent from treatment vessel 210 to solid/liquid separator 220. Separator 220 may be any convenient form of separator such as filter or centrifuge, or settler. Separator 220 is equipped with a solids removal outlet connected to stripper 230 and a liquids outlet 225 connected to a still (not shown). Stripper 230 is equipped with a heater (not shown), vapour off-take line 237 and solids outlet 235. When system 200 is in use, carbonaceous material which has been treated with a fluorine acid solution as described, for example, in United States Patent No. 4,780,112, and solvent are charged into treatment vessel 210 where they are mixed and allowed to remain in contact for sufficient time for at least part of any elemental sulfur present in the carbonaceous materials to be dissolved by the solvent. The solvent is typically ethanol, but may be any other solvent which is capable of dissolving elemental sulfur, or a mixture of such solvents. The treatment in the treatment vessel 210 is typically at ambient temperature and atmospheric pressure. After an appropriate contact time, the contents of treatment vessel 210 are conveyed via bottom outlet 218 to separator 220 in which the solids phase is separated from the solvent phase. The solids phase is transferred to stripper 230 where it is heated, causing residual solvent to evaporate. Suitably, the temperature of heating is at or about the boiling point of the solvent used. After sufficient heating time to cause substantially all of the residual solvent to evaporate from the carbonaceous material in stripper 230, the dried carbonaceous material is discharged via outlet 235 for further processing or for use. Liquids leaving separator 220 and vapour leaving stripper 230 may be passed to a solvent still (not shown) in which the solvent is distilled for recovery and reuse, the other major product in the still being elemental sulfur which is removed for disposal or sale. Example
Coal samples processed by a process as described in United States Patent No.
4,780,112 were dried and examined under an electron microscope. They were observed to contain sulfur in two forms, pyrite and elemental sulfur. A raw high-sulfur coal sample was treated with about twice its weight of 32% w/w aqueous hydrofluorosilicic acid for 30 minutes at ambient temperature, then dried and treated with an aqueous fluorine acid solution as described in United States Patent No. 4,780,112. After separation of the solids they were again dried and examined under the electron microscope. No elemental sulfur was visible.

Claims

Claims
1. A process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising
(a) contacting said materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of said sulfur- containing impurities react with said hydrofluorosilicic acid to form reaction products, and
(b) separating said reaction products from said carbonaceous materials.
2. A process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising
(a) contacting said materials with an aqueous solution of hydrofluorosilicic acid in the absence of hydrogen fluoride under conditions wherein at least some of said sulfur- containing impurities react with said hydrofluorosilicic acid to form reaction products;
(b) separating said reaction products and said hydrofluorosilicic acid from said carbonaceous materials and subsequently
(c) treating said carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride.
3. A process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising: treating said carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, separating said carbonaceous materials from said aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and then contacting said carbonaceous materials with an organic solvent capable of dissolving elemental sulfur.
4. The process of claim 1 or 2 wherein the concentration of hydrofluorosilicic acid in the step (a) is in the range of 27% to 37% (w/v or w/w or v/w).
5. The process of claim 1 or 2 wherein the concentration of hydrofluorosilicic acid in the step (a) is in the range of 28% to 36% (w/v or w/w or v/w).
6. The process of claim 1 or 2 wherein the temperature of step (a) is in the range of 28 to 75°C.
7. The process of claim 1 or 2 wherein the temperature of step (a) is in the range of 30 to 70 °C.
8. The process of claim 1 or 2 wherein the reaction time of step (a) is in the range of 8 to 120 minutes.
9. The process of claim 1 or 2 wherein the reaction time of step (a) is in the range of 10 to 100 minutes.
10. The process of claim 1 or 2 wherein in step (a) the carbonaceous materials are mixed with at least about twice their weight of the aqueous hydrofluorosilicic acid.
11. The process of claim 1 or 2 wherein after step (b) treating said separated carbonaceous materials with further aqueous hydrofluorosilicic acid to remove residual metal fluorosilicates.
12. The process of claim 2 or 3 wherein the fluorine acid solution has a composition lying between the following compositions: 4% w/w H2S1F6, 92% w/w H2O, 4% w/w
HF and 35% w/w H2SiF6, 30% w/w H20, 35% HF.
13. The process of claim 2 or 3 wherein the fluorine acid solution has a composition lying between the following compositions: 5% w/w H2SiF6j 90% w/w H2O, 5% w/w HF and 34% w/w H2SiF6, 32% w/w H2O, 34% HF.
14. The process of claim 2 or 3 wherein the fluorine acid solution has a composition of about 25% w/w H2SiF6, 50% w/w H2O, 25% w/w HF.
15. The process of claim 2 wherein in step (c) the carbonaceous materials are treated with at least about twice their weight of the fluorine acid solution.
16. The process of claim 3 wherein in step (a) the carbonaceous materials are treated with at least about twice their weight of the fluorine acid solution.
17. The process of claim 1 wherein after step (b) comprising washing said separated carbonaceous material with aqueous H2SiF6, and heating said washed carbonaceous material at a temperature in the range of about 250°C to about 400°C to evaporate any residual hydrofluorosilicic acid remaining on the carbonaceous material.
18. The process of claim 3 wherein the organic solvent capable of dissolving elemental sulfur is ethanol, benzene, carbon disulfide, either or carbon tetrachloride, or a mixture of two or more of these.
19. The process of claim 3 wherein the step of contacting the carbonaceous materials with the organic solvent is at ambient temperature and atmospheric pressure.
PCT/AU2003/000258 2002-03-05 2003-03-05 Method for treating carbonaceous materials WO2003074639A1 (en)

Priority Applications (15)

Application Number Priority Date Filing Date Title
AU2003205451A AU2003205451A1 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
NZ535220A NZ535220A (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials to reduce sulphur containing impurities
US10/506,306 US20060150474A1 (en) 2002-03-05 2003-03-05 Method for treatment carbonaceous materials
MXPA04008579A MXPA04008579A (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials.
KR10-2004-7013851A KR20040106285A (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
IL16383503A IL163835A0 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
EP03702221A EP1483360A4 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
EA200401152A EA006065B1 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
CA002477882A CA2477882A1 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials
JP2003573093A JP2005519017A (en) 2002-03-05 2003-03-05 How to treat carbon materials
BR0308198-2A BR0308198A (en) 2002-03-05 2003-03-05 Process for treating carbonaceous materials
UA20041008008A UA77769C2 (en) 2002-03-05 2003-05-03 Process for treatment of carbonaceous materials (variants)
IL163835A IL163835A (en) 2002-03-05 2004-08-31 Method for reducing sulfur content of carbonaceous materials
NO20043674A NO20043674L (en) 2002-03-05 2004-09-02 Process for the treatment of carbonaceous substances
AU2009202202A AU2009202202A1 (en) 2002-03-05 2009-06-03 Method for Treating Carbonaceous Materials

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
AUPS0911 2002-03-05
AUPS0911A AUPS091102A0 (en) 2002-03-05 2002-03-05 Method for treating carbonaceous materials

Publications (1)

Publication Number Publication Date
WO2003074639A1 true WO2003074639A1 (en) 2003-09-12

Family

ID=3834510

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/AU2003/000258 WO2003074639A1 (en) 2002-03-05 2003-03-05 Method for treating carbonaceous materials

Country Status (18)

Country Link
US (1) US20060150474A1 (en)
EP (1) EP1483360A4 (en)
JP (1) JP2005519017A (en)
KR (1) KR20040106285A (en)
CN (1) CN1296465C (en)
AU (3) AUPS091102A0 (en)
BR (1) BR0308198A (en)
CA (1) CA2477882A1 (en)
CO (1) CO5611206A2 (en)
EA (1) EA006065B1 (en)
IL (2) IL163835A0 (en)
MX (1) MXPA04008579A (en)
NO (1) NO20043674L (en)
NZ (1) NZ535220A (en)
PL (1) PL205213B1 (en)
UA (1) UA77769C2 (en)
WO (1) WO2003074639A1 (en)
ZA (1) ZA200407112B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102008010746A1 (en) 2008-02-20 2009-09-03 I-Sol Ventures Gmbh Heat storage composite material

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1976800A1 (en) * 2005-12-14 2008-10-08 Karalee Research PTY Ltd Extraction and purification of minerals from aluminium ores
US8691166B2 (en) 2008-01-08 2014-04-08 Carbonxt Group Limited System and method for activating carbonaceous material
US20090172998A1 (en) * 2008-01-08 2009-07-09 Carbonxt Group Limited System and method for refining carbonaceous material
US8617492B2 (en) * 2008-01-08 2013-12-31 Carbonxt Group Limited System and method for making low volatile carboneaceous matter with supercritical CO2
US8628707B2 (en) * 2008-01-08 2014-01-14 Carbonxt Group Limited System and method for making carbon foam anodes
US20110030270A1 (en) * 2009-08-10 2011-02-10 General Electric Company Methods for removing impurities from coal including neutralization of a leaching solution
CN102424769A (en) * 2011-10-31 2012-04-25 山东科技大学 Chemical desulfurization method for coal
CN109530075B (en) * 2017-09-22 2021-04-13 中南大学 Method for separating and recovering carbon from raw material containing carbon with low cost and high efficiency
CN108455616A (en) * 2017-12-20 2018-08-28 湖北瓮福蓝天化工有限公司 A kind of fluosilicic acid dechlorination method and device
CN112142044B (en) * 2020-09-24 2022-09-30 中南大学 Treatment method of waste lithium ion battery carbon residue

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1537286A (en) * 1921-03-23 1925-05-12 Oscar L Barnebey Process for the manufacture of decolorizing carbons
EP0016624B1 (en) * 1979-03-16 1983-05-25 Kinneret Enterprises Limited Coal de-ashing process
EP0120499A2 (en) * 1983-03-28 1984-10-03 Japan Australia Process Coal Company Method for the removal of iron pyrites from coal and carbon structures during ash removal by chemical means
US4780112A (en) * 1985-02-19 1988-10-25 Oabrand Pty. Limited Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3926575A (en) * 1971-07-19 1975-12-16 Trw Inc Removal of pyritic sulfur from coal
US4441886A (en) * 1982-11-22 1984-04-10 Southern Illinois University Foundation Process for removing organic sulphur from coal and material resulting from the process
GB2158051A (en) * 1983-08-18 1985-11-06 Barron S Whittingham Method for extracting sulphur from coals and lignatic materials

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US1537286A (en) * 1921-03-23 1925-05-12 Oscar L Barnebey Process for the manufacture of decolorizing carbons
EP0016624B1 (en) * 1979-03-16 1983-05-25 Kinneret Enterprises Limited Coal de-ashing process
EP0120499A2 (en) * 1983-03-28 1984-10-03 Japan Australia Process Coal Company Method for the removal of iron pyrites from coal and carbon structures during ash removal by chemical means
US4780112A (en) * 1985-02-19 1988-10-25 Oabrand Pty. Limited Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE102008010746A1 (en) 2008-02-20 2009-09-03 I-Sol Ventures Gmbh Heat storage composite material

Also Published As

Publication number Publication date
IL163835A0 (en) 2005-12-18
AU2003205451A1 (en) 2003-09-16
US20060150474A1 (en) 2006-07-13
JP2005519017A (en) 2005-06-30
NO20043674L (en) 2004-10-06
EA006065B1 (en) 2005-08-25
PL205213B1 (en) 2010-03-31
BR0308198A (en) 2004-12-21
NZ535220A (en) 2005-04-29
EA200401152A1 (en) 2005-02-24
IL163835A (en) 2007-07-24
AU2009202202A1 (en) 2009-06-25
UA77769C2 (en) 2007-01-15
CN1296465C (en) 2007-01-24
MXPA04008579A (en) 2004-12-13
KR20040106285A (en) 2004-12-17
AUPS091102A0 (en) 2002-03-28
CO5611206A2 (en) 2006-02-28
EP1483360A4 (en) 2008-08-20
PL372337A1 (en) 2005-07-11
CN1646669A (en) 2005-07-27
EP1483360A1 (en) 2004-12-08
ZA200407112B (en) 2006-02-22
CA2477882A1 (en) 2003-09-12

Similar Documents

Publication Publication Date Title
AU2009202202A1 (en) Method for Treating Carbonaceous Materials
CA1308232C (en) Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures
EP0016624B1 (en) Coal de-ashing process
JPH05213605A (en) Post-treatment method of generating no waste water in chlorosilane distillation residue
GB2095655A (en) Treating combustion waste gas
AU742408B2 (en) Method for purifying gas loaded with dust
US3386922A (en) Wet air oxidation of combustible materials adsorbed on carbonaceous adsorbent
EP1002763A1 (en) Process and installation for treating a gas containing hydrogen sulfide and sulfur dioxide, including a by-products removing step
AU2010241485A1 (en) Process of Purifying Inorganic Materials
US4482460A (en) Process for removing carbon black from aqueous suspensions
US4250151A (en) Recovery of sulfur from gas streams containing sulfur and sulfur compounds in dilute concentration
US4388172A (en) Liquefaction of coal
CA1075879A (en) Recovery of sulfur from gas streams containing sulfur and sulfur compounds in dilute concentration
AU577686B2 (en) Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures
SU1142145A1 (en) Method of cleaning waste gases of benzol chlorination process
JPH0134922B2 (en)
NO742076L (en)
JPH029728A (en) Method and device for recovering fine quartz glass particle
NO149378B (en) PROCEDURE FOR TREATING A GAS FLOW FOR THE REMOVAL OF SULFUR STEAM
PL177815B1 (en) Method of purifying crude coke oven tar
JPH01165693A (en) Method of purifying coke oven gas
GB2053870A (en) Recovery of sulfur from gas streams containing sulfur and sulfur compounds in dilute concentration
EP0949966A1 (en) Method for treating a catalyst having an active sulphurous phase and contaminated by a mercury compound

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A1

Designated state(s): AE AG AL AM AT AU AZ BA BB BG BR BY BZ CA CH CN CO CR CU CZ DE DK DM DZ EC EE ES FI GB GD GE GH GM HR HU ID IL IN IS JP KE KG KP KR KZ LC LK LR LS LT LU LV MA MD MG MK MN MW MX MZ NO NZ OM PH PL PT RO RU SC SD SE SG SK SL TJ TM TN TR TT TZ UA UG US UZ VC VN YU ZA ZM ZW

AL Designated countries for regional patents

Kind code of ref document: A1

Designated state(s): GH GM KE LS MW MZ SD SL SZ TZ UG ZM ZW AM AZ BY KG KZ MD RU TJ TM AT BE BG CH CY CZ DE DK EE ES FI FR GB GR HU IE IT LU MC NL PT SE SI SK TR BF BJ CF CG CI CM GA GN GQ GW ML MR NE SN TD TG

121 Ep: the epo has been informed by wipo that ep was designated in this application
DFPE Request for preliminary examination filed prior to expiration of 19th month from priority date (pct application filed before 20040101)
WWE Wipo information: entry into national phase

Ref document number: 1-2004-501355

Country of ref document: PH

WWE Wipo information: entry into national phase

Ref document number: 2477882

Country of ref document: CA

Ref document number: 163835

Country of ref document: IL

WWE Wipo information: entry into national phase

Ref document number: 1020047013851

Country of ref document: KR

Ref document number: 2003573093

Country of ref document: JP

Ref document number: PA/a/2004/008579

Country of ref document: MX

Ref document number: 372337

Country of ref document: PL

WWE Wipo information: entry into national phase

Ref document number: 200407112

Country of ref document: ZA

Ref document number: 2004/07112

Country of ref document: ZA

WWE Wipo information: entry into national phase

Ref document number: 535220

Country of ref document: NZ

Ref document number: 2003702221

Country of ref document: EP

WWE Wipo information: entry into national phase

Ref document number: 2705/DELNP/2004

Country of ref document: IN

WWE Wipo information: entry into national phase

Ref document number: 2003205451

Country of ref document: AU

WWE Wipo information: entry into national phase

Ref document number: 1200400977

Country of ref document: VN

WWE Wipo information: entry into national phase

Ref document number: 200401152

Country of ref document: EA

WWE Wipo information: entry into national phase

Ref document number: 20038088428

Country of ref document: CN

WWP Wipo information: published in national office

Ref document number: 2003702221

Country of ref document: EP

WWP Wipo information: published in national office

Ref document number: 1020047013851

Country of ref document: KR

ENP Entry into the national phase

Ref document number: 2006150474

Country of ref document: US

Kind code of ref document: A1

WWE Wipo information: entry into national phase

Ref document number: 10506306

Country of ref document: US

WWP Wipo information: published in national office

Ref document number: 535220

Country of ref document: NZ

WWP Wipo information: published in national office

Ref document number: 10506306

Country of ref document: US