ZA200407112B - Method for treating carbonaceous materials. - Google Patents
Method for treating carbonaceous materials. Download PDFInfo
- Publication number
- ZA200407112B ZA200407112B ZA200407112A ZA200407112A ZA200407112B ZA 200407112 B ZA200407112 B ZA 200407112B ZA 200407112 A ZA200407112 A ZA 200407112A ZA 200407112 A ZA200407112 A ZA 200407112A ZA 200407112 B ZA200407112 B ZA 200407112B
- Authority
- ZA
- South Africa
- Prior art keywords
- acid
- carbonaceous materials
- carbonaceous
- materials
- aqueous
- Prior art date
Links
- 239000003575 carbonaceous material Substances 0.000 title claims description 104
- 238000000034 method Methods 0.000 title claims description 72
- 239000002253 acid Substances 0.000 claims description 80
- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 claims description 46
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 34
- 239000000243 solution Substances 0.000 claims description 27
- 239000000203 mixture Substances 0.000 claims description 26
- 229910052731 fluorine Inorganic materials 0.000 claims description 25
- 239000011737 fluorine Substances 0.000 claims description 24
- 239000000463 material Substances 0.000 claims description 24
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims description 23
- 239000002904 solvent Substances 0.000 claims description 22
- 239000012535 impurity Substances 0.000 claims description 20
- 239000007864 aqueous solution Substances 0.000 claims description 18
- 229910052717 sulfur Inorganic materials 0.000 claims description 18
- 239000011593 sulfur Substances 0.000 claims description 18
- 229910000040 hydrogen fluoride Inorganic materials 0.000 claims description 15
- 229910052751 metal Inorganic materials 0.000 claims description 13
- 239000002184 metal Substances 0.000 claims description 13
- 239000007795 chemical reaction product Substances 0.000 claims description 12
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical group CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 10
- 238000010438 heat treatment Methods 0.000 claims description 8
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 claims description 6
- 239000003960 organic solvent Substances 0.000 claims description 6
- RPAJSBKBKSSMLJ-DFWYDOINSA-N (2s)-2-aminopentanedioic acid;hydrochloride Chemical class Cl.OC(=O)[C@@H](N)CCC(O)=O RPAJSBKBKSSMLJ-DFWYDOINSA-N 0.000 claims description 5
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 claims description 5
- 230000035484 reaction time Effects 0.000 claims description 5
- VZGDMQKNWNREIO-UHFFFAOYSA-N tetrachloromethane Chemical compound ClC(Cl)(Cl)Cl VZGDMQKNWNREIO-UHFFFAOYSA-N 0.000 claims description 5
- 238000005406 washing Methods 0.000 claims description 5
- 229910004072 SiFe Inorganic materials 0.000 claims description 2
- QGJOPFRUJISHPQ-NJFSPNSNSA-N carbon disulfide-14c Chemical compound S=[14C]=S QGJOPFRUJISHPQ-NJFSPNSNSA-N 0.000 claims description 2
- JGFZNNIVVJXRND-UHFFFAOYSA-N N,N-Diisopropylethylamine (DIPEA) Chemical compound CCN(C(C)C)C(C)C JGFZNNIVVJXRND-UHFFFAOYSA-N 0.000 claims 1
- 229910052500 inorganic mineral Inorganic materials 0.000 claims 1
- 150000002500 ions Chemical class 0.000 claims 1
- 239000011707 mineral Substances 0.000 claims 1
- 239000007789 gas Substances 0.000 description 32
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 31
- QPJSUIGXIBEQAC-UHFFFAOYSA-N n-(2,4-dichloro-5-propan-2-yloxyphenyl)acetamide Chemical compound CC(C)OC1=CC(NC(C)=O)=C(Cl)C=C1Cl QPJSUIGXIBEQAC-UHFFFAOYSA-N 0.000 description 27
- 239000007787 solid Substances 0.000 description 27
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 22
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 16
- 229960005349 sulfur Drugs 0.000 description 16
- 239000008346 aqueous phase Substances 0.000 description 15
- 235000001508 sulfur Nutrition 0.000 description 15
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 14
- 229910052799 carbon Inorganic materials 0.000 description 12
- 239000007788 liquid Substances 0.000 description 12
- 238000002156 mixing Methods 0.000 description 12
- 239000006096 absorbing agent Substances 0.000 description 8
- 238000012545 processing Methods 0.000 description 8
- 239000000377 silicon dioxide Substances 0.000 description 8
- 208000005156 Dehydration Diseases 0.000 description 7
- 230000018044 dehydration Effects 0.000 description 7
- 238000006297 dehydration reaction Methods 0.000 description 7
- 238000001035 drying Methods 0.000 description 7
- 229910001512 metal fluoride Inorganic materials 0.000 description 7
- 238000000746 purification Methods 0.000 description 7
- 238000006243 chemical reaction Methods 0.000 description 6
- 239000003245 coal Substances 0.000 description 6
- 239000008246 gaseous mixture Substances 0.000 description 6
- ABTOQLMXBSRXSM-UHFFFAOYSA-N silicon tetrafluoride Chemical compound F[Si](F)(F)F ABTOQLMXBSRXSM-UHFFFAOYSA-N 0.000 description 6
- 229910004014 SiF4 Inorganic materials 0.000 description 5
- 238000010586 diagram Methods 0.000 description 5
- 229910044991 metal oxide Inorganic materials 0.000 description 5
- 150000004706 metal oxides Chemical class 0.000 description 5
- KLZUFWVZNOTSEM-UHFFFAOYSA-K Aluminium flouride Chemical compound F[Al](F)F KLZUFWVZNOTSEM-UHFFFAOYSA-K 0.000 description 4
- 239000011260 aqueous acid Substances 0.000 description 4
- 150000002739 metals Chemical class 0.000 description 4
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 4
- 229910052815 sulfur oxide Inorganic materials 0.000 description 4
- MBMLMWLHJBBADN-UHFFFAOYSA-N Ferrous sulfide Chemical compound [Fe]=S MBMLMWLHJBBADN-UHFFFAOYSA-N 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 3
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 3
- 239000003077 lignite Substances 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 239000013557 residual solvent Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 238000000638 solvent extraction Methods 0.000 description 3
- 239000000725 suspension Substances 0.000 description 3
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 239000005864 Sulphur Substances 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000001419 dependent effect Effects 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 229910001504 inorganic chloride Inorganic materials 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000012071 phase Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 230000002285 radioactive effect Effects 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- BHHYHSUAOQUXJK-UHFFFAOYSA-L zinc fluoride Chemical compound F[Zn]F BHHYHSUAOQUXJK-UHFFFAOYSA-L 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 239000004411 aluminium Substances 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 1
- 239000003830 anthracite Substances 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 150000002222 fluorine compounds Chemical class 0.000 description 1
- 125000001153 fluoro group Chemical group F* 0.000 description 1
- 239000007792 gaseous phase Substances 0.000 description 1
- 239000010439 graphite Substances 0.000 description 1
- 229910002804 graphite Inorganic materials 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 229910003480 inorganic solid Inorganic materials 0.000 description 1
- FZGIHSNZYGFUGM-UHFFFAOYSA-L iron(ii) fluoride Chemical compound [F-].[F-].[Fe+2] FZGIHSNZYGFUGM-UHFFFAOYSA-L 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- 229910052976 metal sulfide Inorganic materials 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- NIFIFKQPDTWWGU-UHFFFAOYSA-N pyrite Chemical compound [Fe+2].[S-][S-] NIFIFKQPDTWWGU-UHFFFAOYSA-N 0.000 description 1
- 229910052683 pyrite Inorganic materials 0.000 description 1
- 239000011028 pyrite Substances 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000012958 reprocessing Methods 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 239000012798 spherical particle Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 125000004434 sulfur atom Chemical group 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- QHMQWEPBXSHHLH-UHFFFAOYSA-N sulfur tetrafluoride Chemical compound FS(F)(F)F QHMQWEPBXSHHLH-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS 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
- C10L9/00—Treating solid fuels to improve their combustion
- C10L9/02—Treating solid fuels to improve their combustion by chemical means
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)
Description
Le
Method For Treating Carbonaceous Materials
Technical Field } The invention relates to methods for treating carbona ceous materials to remove or substantially decrease the amount of non-carbonaceous impurities therein.
Background of the Inventio n
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;SiFs) and hydrofluoric acid (HF), whereby metal oxides in the carbon are converted to metal fluorides and/or metal fluorosilicates, from which carbon is then seprarated. 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-containingg impurities is treated by the process of United States Patent No. 4,780,112, the purified carbon is still contaminated with sul fur. The present inventor has surprisingly discovere=d that the remaining sulfur is present as elemental sulfur, which in some circumstances as visible when the carbon is viewed wander 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 thes sulfur into sulfur oxides. As a result, the flue gases generated by the combustion of the c-arbon need to be scrubbed or otherwise substantially freed of the sulfur oxides before theey can be discharged into the atmosphere if release of sulfur oxides into the environment iss to be avoided.
Accordingly, there is a need for an improved proce=ss for treating carbonaceous material s to decrease the amount of non-carbonaceous impur-ities therein, and in particular there is & need for an improved process for removing or at lesast substantially reducing the amount ©f sulfur in carbonaceous materials.
Surprisingly, the present inventor has discovered that the amount of sulfur- . containimg impurities in carbonaceous materials can be substantially decreased by a process which involves treating the carbonaceous materials with an aqueous solution of hydroflmorosilicic acid, or with an organic solvent capable of dissolving elemental sulfur.
Summary of the Invention i According to a first embodiment of the invention thesre 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 s ulfur-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 tinere is provided a process for reducing the amount of sulfur-containing impurities on carbonaceous materials, c-omprising (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- c-ontaining 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 flexorine acid solution which c.omprises 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 dn carbonaceous materials, comprising treating the carbonaceous materials with a fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, seeparating the carbonaceous materials from the aqueous s-olution of hydrofluorosilicic a~cid and hydrogen fluoride, and then contacting the carbeonaceous materials with an o rganic solvent capable of dissolving elemental sulfur.
As used herein, the term “carbonaceous materials” i.s 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 axd the like.
As used herein, unless the context clearly indiccates otherwise, the words "ecomprise", "comprises", "comprising" or other variations tlaereof 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 Descripti on of the Invention ’ In the processes of the first and second embodiments of the invention, the s concentration of hydrofluorosilicic acid in the step of contacting the materials with an aqueous solution of hydrofluorosilicic acid winder 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 372% (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 atsout 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 times 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 acqueous 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 furst 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 re latively purified carbonaceous materials. Optionally, the filtered relatively purified carboriaceous : materials may be treated with further aqueous hydrofluorosilicic acid, typically h aving 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 xemoved 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. 4,780,1 12, 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 fluorime acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hysdrogen 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.
In 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 H,SiFs, 92% w/w HO, 4% w/w HF and 35% w/w
H,SiFs, 30% w/w H20, 35% HIF. In step (c) of the process of the second embo«diment, and in the process of the third embodiment, the fluorine acid solution typicallwy has a 2s composition lying between the following compositions: 5% w/w H;SiFs, 90% w/v H;0, 5% w/w HF and 34% w/w H,SiFg, 32% w/w Hy0, 34% HF. More typically the composition of the fluorine acid solution is about 25% w/w H,SiFg, 50% w/w H,€, 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 100k=Pa 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 betweem silica present in the carboraceous materials and hydrogen fluoride. In step (c) the minimum quantity of the fluorine acid solution employed is typically enougln to enable the mixture of it and the carbonaceous materials to be stirred. Usually, the carb onaceous materials are mixed with at least about twice their weight of the fluorine acid solution. More usually, s the fluorine acid soltation is present in an amount of from about 7€% to 90% by weight, relative to the total w=eight 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 hydro-fluorosilicic acid and hydrogen fluoride, thme mixture of the carbonaceous material and thee 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 tos HF and SiF4) or other relatively dense impurities to be capable of being separated from time bulk of the relatively purified carbonaceows 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,SiFg, separated, dried t« remove excess water (at about 100-110°C) and heated to a temperature within the rarge of about 250°C to 400°C, or 280°C to 340°C, typically about 310°C, to ewaporate any residual hydrofluorosilicic ac-id remaining on the carbonaceous material, be=fore 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 matesrials after it has been contacted with therm is relatively enriched in SiF; and depleted im HF, compared to the fluorine acid solutiom before it is contacted with the carbonaceous materials, as a result of the reaction:
SiO; + 4HF — SiF,4 + 2H,0.
This spent aqueous phase, if is recycled to the step of besing contacted with the relatively purified c arbonaceous material, thus tends to reach a point where it becomes saturated with respect to SiF,, at which point any further SiF; generated as a result of further reaction is ewolved as a gas. Conveniently, the reactor in which the fluorine acid solution is contacted with the relatively purified carbonaceous materials includes a means for SiF, to be remowed from it. Suitably, the spent aqueous phase from this step may be
’ WO» (3/074639 PCT/AU03/00258
Airected to a holding vessel where any excess SiF, dis vented from it. The concentration of
EJF in the spent aqueous phase may be increased by directing a gaseous mixture of HF ) and SiF, into the vessel, whereby the HF is absorbexd and the SiF, passes through. Vented
SiF, is conveniently directed to a hydrolyser where it is treated with water to produce s HEI,SiFs, and SiO; according to the equation 3SiF, + 2H,0 — 2H,SiF¢ + SiO;
The silica so produced may be separated fr-om 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 directesd to an acid still in which the streams are combined and distilled. A gaseous mixture of water, HF and SiF, is distilled from the still, these substances being more volatile than the 32% w/w aqueous hydrofluorosilicic acid azeotrope. The gaseous mixture of water, EHF 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 SiF, may be separated by directing it to a holding vessel which contains a solution of H,SiFg that is saturated with respect to SiF,, as described above.
Suitably, the dehydration step for a gase<ous mixture of water, HF and SiF, comprises contacting the gases with a sufficient quantity of anhydrous metal fluoride such as AlF; to absorb all the water present. Other meetal fluorides that can be used include zinc fluoride and ferrous fluoride. Substantially arahydrous gases may be obtained in this wvay, 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 H,SiFs. Gaseous HCl, derived from imorganic 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
HIF, SiF,, steam, HCI and sulfur dioxide to be evolved, and so as to cause any metal fluorosilicates present to be concentrated above tRaeir solubility limit and to separate as
. W 0 03/074639 PCT/AU03/00258 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 perocess as described above, by contacting it with anhydrous aluminium fluoride, and subsequently passed to an activated carbon filter for removal of sulfur oxides and HCl. 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.
In the process of the third embodiment the process nay further comprise after the separating: washing the carbonaceous materials to remove any ressidual 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 tetrachloride, 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 clevated tempera-tures (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 atm), or both, may also be used. The quantity of solvent used is not critical, but a minimum quantity for practical purposes is a quantity sufficient to enable the mixtiare 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 tlne carbonaceous material with the fluorine acid solution, to be dissolved. Conveniently, thes 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 treeated 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).
¢ WO 03./074639 PCT/AU03/00258
The step of separating in the embodiments of the invention may comprise filtering, separating by centrifuging or other suitable separating m_eans.
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 obstainable by the process of United
States Patent No. 4,780,112, processes of the present in=vention 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 rmercury and radioactive elements, and inorganic chlorides. For example, if coal contained sulphur at about 8wi% it may be possible to remove this sulphur to a lower level (e.g. ab out or less than 2wt% or about or less than 1 wt% or about or less than 0.5wt%) by sub-jecting the coal to one (or more) cycles of the processes of the first to third embodimentss. Removal of inorganic chlorides, mewcury and radioactive elements, in particular, is mome effective with a process of the second embodiment, than with the process of Uniteed States Patent No. 4,780,112.
Further, processes of the present invention can lower t he 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 carbonaceouas materials may reduced prior to the treating step to granular form which is less than abowat4, 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 mayy 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 mnay be treated in its raw form. If the carbonaceous material contains excess moisture it rnay be dried (e.g. at 60-120°C or 100-120°C) prior to processing so as to remove exce=ss moisture. The drying may be coraducted 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 S% 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 driecd (e.g. at 60-120°C or 100-120°C) . prior to processing by passing hot air over the carbona<ceous 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 combuasst.
Figure 1 is a schematic block diagram of a system for purificatieon and combustion of carbonacesous material, incorporating a process in accordance with the present ] invention.
Figure 2 is a schematic block diagram of a still and associated pelant for processing an aqueous seolution 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 treatme=nt 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 combust3on of carbonaceous materials, incorporating a process i n accordance with the present in vention.
Referrimg to Figure 1, system 10 includes hopper 20 fox holding impure carbonaceous materials which have been reduced to granular form, preferably substantially spherical particles and preferably less than about 2mrm in particle size.
Associated w=ith 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 a_n aqueous solution of approxima-tely 32%w/w H,SiFe from a hydrolyser 32. Purification reeactor 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 2s reactor 30, after the carbonaceous material has been in contact with tEie aqueous H,SiF, 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 fT lter 50 are transferred to silica removal reactor 55. Reacstor 55 is equipped with line 58 for admitting an aqueous fluorine acid solution of HF an-d H,SiFs 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 65A, 65B, the first stagze 65A of which is capable of being agitated ) ultrasonically. The distal end of reactor &5B discharges into separator 16 which is equipped with takeoffs 66 and 67 adjacent i&s 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 so-lution. 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 o¥ 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 miximxg 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 systerm 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 connec:ted 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 &7 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 transferred via feed unit 25 to reactor 30. Suitably, the transfer of carbonaceous material via feed unit 25
° WO 03/074639 PCT/AU03,700258 1s 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 H,SiFs, from hydrolyser 32 via line 24. IReactor 30 is typically at a temperature of about 30°C and atmospheric pressure.
Carbonaceous material is comtacted with the aqueous H,SiF in reactor 30» for a time sufficient for at least some of amy 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 batchwwise, 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 S50 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 bw 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 a«queous fluorine acid solution comprising aqueous hydrofluorosilicic acid and hydrogen fluoride so that partially purified carbonaceous 2s materials from purification reactosr 30 can remain in contact with the aqueous fluorine acid solution for a sufficient time for at least some of any silica in the partial xy purified . carbonaceous material to be dissol-ved. Reactor 55 is typically maintained at a pressure in the range of about 100-135 kPa ard a temperature of about 70°C. Residence time of the carbonaceous material in reactor 35 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 v WO 03/074639 PCT/AU03/0 0258 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 65A the suspension of ) carbonaceous materi al in aqueous acid is agitated sufficiently for any FeS amd other } relatively dense material present to be separable at separator 16 at the end of second stage 5s 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 Jin FeS is removed via line 67 . A slurry of carbonaceous material in aqueous hydroflucrosilicic acid is removed fromm an upper portion of separator 16 via line 66 and trans ferred to centrifuge or belt filter 70 where aqueous acid is removed, leaving a carbonaceous material stream to be- transferred to the washer/separator system.
In this system. carbonaceous material is washed with aqueous hydrofluerosilicic acid which flows through the system in the opposite direction to the direction o f flow of the carbonaceous ma terials. That is, the fresh supply of aqueous hydrofluorosilicsic acid is supplied from hydroRyser 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 whexe it is mixed with carbonaceous material entering that mixzing tank, and separated therefwom in separator 74. The aqueous phase separated in separator 74 is transferred to mixirmg tank 71 where it is mixed with carbonaceous materia l leaving centrifuge or belt filter 70. The solids and liquids in mixing tank 71 are sepsarated 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 c onsists of mixing vessel 77 amd steel tube reactor 78. The carbonaceous material enterirag mixing vessel 77 is mixed with oxygen-depleted combustion gases and transferred to r-eactor 78 . where it is baked under inert atmosphere, typically at about 310°C, to remmove the remaining hydrofluorosilicic acid from the surface of the carbonaceous matemrial. The - hydrofluorosilicic acid is removed as gaseous hydrogen fluoride and silicon tetr-afluoride, together with stearrm, which gases are directed to still 80 after the gases and the dried solids are separatec] 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 c arbonaceous materials storage container 93 from whdch dried carbonaceous material can be supplied #o furnace and gas turbine system 95. Optio nally, system 10 includes a solvent extraction stage as described below with reference to Figure i 3, between separator 79 and storage con tainer 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 EIF 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, gases from system 1 00 as illustrated in Figure 2 and described in mmore detail below. Gases leaving HF absorber 54 pass to hydrolyser 32 to which water 36s is added in sufficient amount to produce aqueous
H,SiF 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 transfermred to still 80 where it is heated to sufficient temperature (typically 105 to 110 °C) to cause hydrogen fluoride and silicon tetrafluori de 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 frorm still 80 via separator 98. Still 80 is typically heated by exhaust gas from gas turbime 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 AlF;. The mixture is passed thxough tubular dehydration reactor 84 leading #o removal of substantially all the water fromm the gaseous phase, thereby producing a subdstantially anhydrous gaseous mixture of HIF and 2s SiF4 which is transferred from dehydr ation reactor 84 to HF absorber 54 via lime 87.
Moist AlF; produced in dehydration reactor 84 is transferred to AlF; drier 89 in which the . moist AlF; is heated. Water vapour generated by this heating is removed at 91a andl 91b, and substantially anhydrous AlFj; 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 zqueous solution or suspension produced bys step (a) of a process of the first or second em bodiments 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 1240 and a bottom outlet connected to level controlled separator 150. Gas outlet 120 cormmunicates 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 sw fficient for gases comprising HF, SiF,, sulfur dioxide and water vapour to be evolved frorm 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 systern 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 Es 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 HCI, are absorbed by the activated carbon, generating a streamn of gaseous HF and SiF, 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, s% and any HCI 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 t= 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 pl ant 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 c apable of dissolving elemental sulfur, in accordance with a process of the third embodimemt 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 fiom treatment vessel 210 to solid/liquid separator 220. Separator 220 may be any conve=nient 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-tamke line 237 and solids outlet 235. 1s 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 21 0 where they are mixed and allowed to remain in contact for sufficient time for at least pwart 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 phamse. 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 clistilled for recovery and reuse, the other major product in the still being elemental sulfur which is removed for disposal or sale.
v WO 03/074639 PCT/AU03/00258
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 w-ith about twice its weight of 32% w/w aqueous hydrofluorosilicic acid for 30 minutes aE 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 (19)
- + 2 SEP. 2007 19:39 SPRUSON ANC FERGUSON €129261586 NO. 7400, F. 39/39 rCT/AUVowoz58 1 April 2004 ° ” Claims l. A process for reducing the amount of sulfur-containing impurities in carbonaceous materials, comprising (a) contacting said materials with an aqueous solu tion of hydrofluorosilicic acid in s the absence of hydrogen fluoride and a strong mineral acid under conditions wherein at least some of said sulfur-containing impurities react wisth said hydrofluorosilicic acid to form reaction products, and (b) separating said reaction products from said carbwonaceous materials.
- 2. A process for reducing the amount of sulfur-conta ining impurities in carbonaceous=. 10 materials, comprising (2) contacting said materials with an aqueous solumtion of hydrofluorositicic 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 h-ydrofluorosilicic acid from said 1s carbonaceous materials and subsequently (¢) treating said carbonaceous materials with @ fluorine acid solution which comprises an aqueous solution of hydrofluorosilicic acid =and hydrogen fluoride.
- 3. A process for reducing the amount of sulfur-contafining impurities in carbonaceous materials, comprising: ) 20 treating said carbonaceous materials with a fluerin, e acid solution which comprises an aqueous solution of hydrofluorosilicic acid and hydrog=en fluoride, separating said carbonaceous materials fromm said aqueous solution of hydrofluorosilicic acid and hydrogen fluoride, and then contacting said carbonaceous materials with a-n organic solvent capable of 2s dissolving elemental sulfur. .
- 4. The process of claim 1 or 2 wherein the concentra@ion 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 concentra€ion of hydrofluorosilicic acid in the step (a) is in the range of 28% to 36% (w/v or w/w or ~v/w), AMENDED SHEET IPEA/AL [1\DayLib\LIBXX\LIoyd|Cen2PCTV1 doc:FM
- 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 whereim 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 wheredn the reaction time of step (a) is in the range off to 100 minutes.
- 10. The process of claim 1 or 2 whexein in step (a) the carbonaceous materials are 10 mixed with at least about twice thei r weight of the aqueous hydrofluorosilicic acid.
- 11. The process of claim 1 or 2 vwherein after step (b) treating said separated carbonaceous materials with furtlaer aqueous hydrofluorosilicic acid to removes residual metal fluorosilicates.
- 12. The process of claim 2 or 3 wherein the fluorine acid solution has a composition lying between the following compo sitions: 4% w/w H,SiFg 92% w/w H,0, 4% w/w- HF and 35% w/w H,SiFe, 30% w/w» H,0, 35% HF.
- 13. The process of claim 2 or 3 wherein the fluorine acid solution has a composition. lying between the following compo sitions: 5% w/w H,SiFs 90% w/w H,0, 5% w/w HF and 34% w/w H,SiFg, 32% w/w H,0, 34% HF.
- 14. The process of claim 2 or 3 wherein the fluorine acid solution has a composition of” about 25% w/w H,SiFs, 50% w/w H,0, 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 H,SiF¢, and heating said washed carbonaceous material at a temperature in the ran ge of about 250°C to about 400°C to evaporate any residual hydrofluorosilicic acid remaining on the carbonaceous material.L 4
- 18. The process of claim 3 wherein the orgzanic solvent capable of dissolving elemental sulfur is ethanol, benzene, carbon dis ulfide, 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 tesmperature and atmospheric pressure.
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AUPS0911A AUPS091102A0 (en) | 2002-03-05 | 2002-03-05 | Method for treating carbonaceous materials |
Publications (1)
Publication Number | Publication Date |
---|---|
ZA200407112B true ZA200407112B (en) | 2006-02-22 |
Family
ID=3834510
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
ZA200407112A ZA200407112B (en) | 2002-03-05 | 2004-09-06 | 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) |
Families Citing this family (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
BRPI0619870A2 (en) * | 2005-12-14 | 2011-10-25 | Karalee Res Pty Ltd | extraction and purification of minerals from aluminum ores |
US8628707B2 (en) * | 2008-01-08 | 2014-01-14 | Carbonxt Group Limited | System and method for making carbon foam anodes |
US8617492B2 (en) * | 2008-01-08 | 2013-12-31 | Carbonxt Group Limited | System and method for making low volatile carboneaceous matter with supercritical CO2 |
US20090172998A1 (en) * | 2008-01-08 | 2009-07-09 | Carbonxt Group Limited | System and method for refining carbonaceous material |
US8691166B2 (en) | 2008-01-08 | 2014-04-08 | Carbonxt Group Limited | System and method for activating carbonaceous material |
DE102008010746A1 (en) | 2008-02-20 | 2009-09-03 | I-Sol Ventures Gmbh | Heat storage composite material |
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 |
Family Cites Families (7)
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 |
US3926575A (en) * | 1971-07-19 | 1975-12-16 | Trw Inc | Removal of pyritic sulfur from coal |
AU5623680A (en) * | 1979-03-16 | 1980-09-18 | Kinneret Enterprises Ltd. | De-ashing 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 |
AU2620084A (en) * | 1983-03-28 | 1984-10-04 | Oabrand Pty. Ltd. | Removal of iron pyrites from coal with hydrofluoric acid |
GB2158051A (en) * | 1983-08-18 | 1985-11-06 | Barron S Whittingham | Method for extracting sulphur from coals and lignatic materials |
WO1986004917A1 (en) * | 1985-02-19 | 1986-08-28 | Oabrand Pty. Limited | Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures |
-
2002
- 2002-03-05 AU AUPS0911A patent/AUPS091102A0/en not_active Abandoned
-
2003
- 2003-03-05 CA CA002477882A patent/CA2477882A1/en not_active Abandoned
- 2003-03-05 BR BR0308198-2A patent/BR0308198A/en not_active IP Right Cessation
- 2003-03-05 EA EA200401152A patent/EA006065B1/en not_active IP Right Cessation
- 2003-03-05 US US10/506,306 patent/US20060150474A1/en not_active Abandoned
- 2003-03-05 KR KR10-2004-7013851A patent/KR20040106285A/en not_active Application Discontinuation
- 2003-03-05 IL IL16383503A patent/IL163835A0/en not_active IP Right Cessation
- 2003-03-05 WO PCT/AU2003/000258 patent/WO2003074639A1/en active Application Filing
- 2003-03-05 EP EP03702221A patent/EP1483360A4/en not_active Withdrawn
- 2003-03-05 NZ NZ535220A patent/NZ535220A/en not_active IP Right Cessation
- 2003-03-05 AU AU2003205451A patent/AU2003205451A1/en not_active Abandoned
- 2003-03-05 JP JP2003573093A patent/JP2005519017A/en active Pending
- 2003-03-05 PL PL372337A patent/PL205213B1/en not_active IP Right Cessation
- 2003-03-05 CN CNB038088428A patent/CN1296465C/en not_active Expired - Fee Related
- 2003-03-05 MX MXPA04008579A patent/MXPA04008579A/en unknown
- 2003-05-03 UA UA20041008008A patent/UA77769C2/en unknown
-
2004
- 2004-08-31 IL IL163835A patent/IL163835A/en unknown
- 2004-09-02 NO NO20043674A patent/NO20043674L/en not_active Application Discontinuation
- 2004-09-06 ZA ZA200407112A patent/ZA200407112B/en unknown
- 2004-09-23 CO CO04094964A patent/CO5611206A2/en not_active Application Discontinuation
-
2009
- 2009-06-03 AU AU2009202202A patent/AU2009202202A1/en not_active Abandoned
Also Published As
Publication number | Publication date |
---|---|
EA200401152A1 (en) | 2005-02-24 |
NO20043674L (en) | 2004-10-06 |
WO2003074639A1 (en) | 2003-09-12 |
AUPS091102A0 (en) | 2002-03-28 |
CO5611206A2 (en) | 2006-02-28 |
MXPA04008579A (en) | 2004-12-13 |
AU2009202202A1 (en) | 2009-06-25 |
BR0308198A (en) | 2004-12-21 |
CN1296465C (en) | 2007-01-24 |
NZ535220A (en) | 2005-04-29 |
AU2003205451A1 (en) | 2003-09-16 |
PL372337A1 (en) | 2005-07-11 |
PL205213B1 (en) | 2010-03-31 |
CN1646669A (en) | 2005-07-27 |
UA77769C2 (en) | 2007-01-15 |
KR20040106285A (en) | 2004-12-17 |
EP1483360A4 (en) | 2008-08-20 |
IL163835A (en) | 2007-07-24 |
JP2005519017A (en) | 2005-06-30 |
EP1483360A1 (en) | 2004-12-08 |
CA2477882A1 (en) | 2003-09-12 |
IL163835A0 (en) | 2005-12-18 |
EA006065B1 (en) | 2005-08-25 |
US20060150474A1 (en) | 2006-07-13 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
AU2009202202A1 (en) | Method for Treating Carbonaceous Materials | |
GB2095654A (en) | Treating combustion waste gas | |
JPH0275397A (en) | Treatment of waste water contaminated with volatile compound | |
CA1308232C (en) | Method for the continuous chemical reduction and removal of mineral matter contained in carbon structures | |
CN1986390A (en) | Process of purifying and recovering waste sulfuric acid containing organic impurity | |
US9216904B2 (en) | Recovery of sulfur from sulfur-containing waste | |
JPH05213605A (en) | Post-treatment method of generating no waste water in chlorosilane distillation residue | |
GB2095655A (en) | Treating combustion waste gas | |
CN116371875A (en) | System and method for treating waste incineration fly ash | |
CA2229945A1 (en) | Method for purifying gas loaded with dust | |
US3386922A (en) | Wet air oxidation of combustible materials adsorbed on carbonaceous adsorbent | |
CA2030253A1 (en) | Process for the treatment of hot waste gas containing hydrogen chloride | |
CN113666376A (en) | Recycling treatment method for silicon slag | |
AU2010241485A1 (en) | Process of Purifying Inorganic Materials | |
US4482460A (en) | Process for removing carbon black from aqueous suspensions | |
BE1006044A6 (en) | Method for obtaining cellulose powder. | |
US4250151A (en) | Recovery of sulfur from gas streams containing sulfur and sulfur compounds in dilute concentration | |
SU971805A1 (en) | Process for purifying effluents from epoxy resin production | |
JP3854652B2 (en) | Method for producing calcium hydroxide | |
CA1075879A (en) | Recovery of sulfur from gas streams containing sulfur and sulfur compounds in dilute concentration | |
CN117585689A (en) | Method for preparing sodium bicarbonate and co-producing potassium sulfate and ammonium chloride from sodium sulfate waste salt | |
JPH1161149A (en) | Removal of halogen compound in heat-decomposed gas | |
CN114772638A (en) | Chloride dewatering and purifying method | |
JPH0134922B2 (en) | ||
CN118062846A (en) | Carbonization treatment of alkylated waste acid and method for preparing activated carbon |