IPC classes for russian patent Complex processing of coal combustion flue ash. RU patent 2502568. (RU 2502568):
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Method of obtaining coagulant-flocculant / 2471720
Invention can be used in purification of natural water and industrial sewage. To realise the method decomposition of alumosilicate-containing raw material with sulfuric and hydrochloric acid with further separation of obtained solution from reaction mass and introduction in it of additional reagent, until target product is obtained. During decomposition of alumosilicate-containing raw material inorganic fluorine-containing compound is additionally introduced into reaction mass. As additional reagent, water solution of inorganic salt of trivalent metal is used. As inorganicfluorine-containing compound, used is sodium fluoride, water solution of hydrofluoric acid or hexafluorosilicic acid, and as inorganic salt of trivalent metal, used is trivalent iron chloride.
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Method of producing composite alumosilicic flocculant-coagulant / 2447021
Invention can be used to purify water from different types of contaminants. The first step of the method involves mixing initial components - aluminium sulphate, anhydrous sodium sulphate, sodium hydrogen sulphate or aluminium sulphate, sodium hydrogen sulphate, or aluminium sulphate, anhydrous sodium sulphate and 96% concentrated sulphuric acid. At the second step, monosil with modulus 1.5-3.0 is added to the obtained mixture while stirring, with the following ratio of components, respectively, pts.wt: 3.4:2.1:1.4:1, or 3.4:1.4:1, or 3.4:2.9:0.6:1. The obtained crystalline product has high stability and effectiveness, long storage life of up to 12 months and can be easily transported. Concentration of active components in the dry powder of the flocculant-coagulant is equal to 57-75%.
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Procedure for extraction of aluminium and iron from ash-and-slag waste / 2436855
Procedure for extraction of aluminium and iron from ash-and-slag waste consists in treatment with solution of sulphuric acid and in extraction of aluminium containing components into solution. Before extraction of aluminium containing components into solution waste is subjected to classification and multi-stage magnetic separation at periodic increase of field of magnetic induction for complete extraction of magnetic fraction containing iron.
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Method of producing alumosilicic coagulant-flocculant / 2421400
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Method of producing aluminium sulphate from burnt kaolin clay / 2402487
Invention relates to chemical industry and non-ferrous metallurgy and can be used to produce aluminium sulphate in liquid form. To obtain aluminium sulphate, burnt kaolin clay is reacted with sulphuric acid taken in stoichiometric amount of 93-95%. The reaction is carried out in a reactor consisting of two parts - a lower part with diametre to height ratio of 0.4-0.5 and an upper part with diametre to height ratio of 2.3-2.5, while stirring the pulp with a propeller mixer turning at 40-80 rpm and jet steam at pressure of 1.5-3.5 atm, temperature of 110-125°C for 30-45 minutes. The melt formed is diluted with water until achieving Al2O3 concentration of 7.2%.
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Method of aluminium-containing coagulant obtainment / 2392228
Aluminium-containing coagulant based on aluminium sulphate is obtained by dissolution of metal waste of aluminium production in sulphuric acid solution of 100-200 g/l concentration at 65°C and with application of symmetrical alternate current of commercial frequency and current density of 0.2-0.3 A/cm2.
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Method of obtaining alumosilicon flocculant-coagulant and water purification method using said flocculant-coagulant / 2388693
Invention relates to processing alumosilicon material to obtain inorganic alumosilicon flocculant-coagulant and using the said flocculant-coagulant to purify water in household and industrial systems. To realise the method of obtaining the flocculant-coagulant, alumosilicon material is treated in an aqueous sulphuric acid medium. The liquid phase is separated from the solid phase and dehydrated. The material is treated with concentrated 96% sulphuric acid in components ratio which ensures production of 20-30 % aqeous solution of flocculant-coagulant. The obtained concentrated aqueous solution of flocculant-coagulant is dehydrated to obtain a dry product through vacuum evaporation at temperature below the boiling point of water or through dispersion in the high-temperature stream of a heat carrier gas. The method of purifying water using an alumosilicon flocculant-coagulant is realised in the presence of an activating air additive with subsequent separation of the formed residue. Alumosilicon flocculant-coagulant is used in powder form in amount of 50-100 mg/l or 0.1-2.0 % aqueous solution in amount of 25-100 mg/l.
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Method of receiving of aluminium sulfate / 2355639
Invention relates to hydrometallurgy field, particularly to methods of processing of high-silicon aluminium raw materials with receiving of aluminium sulfate. Method includes treatment of aluminium-bearing raw materials - kaolin 95% sulfuric acid and thermal processing of the received reactionary mass. It is used kaolin with mass concentration of alumina, equal to 20-27%, which before blending with sulfuric acid is moistened. Thermal processing of reactionary mass is implemented at 320-350°C during 3 hours, after it sulfate product is leached by water at ratio S:L, equal to 1:3, and temperature 80-90°C up to finite size pH, equal to 3.5-4.0. Received pulp is filtered, filtrate evaporated up to density 1.45 g/cm3 and aluminium sulfate is crystallised.
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Method of production of aluminum sulfate / 2315715
The invention is pertaining to the technology of obtaining of production of the aluminum sulfate, which is used as the coagulum at purification of the economic-drinking, industrial and the waste waters in the industrial and technological processes and may be used at the enterprises engaged in the reprocessing of the primary piles aluminum-containing slag. The method of production of the aluminum sulfate provides for the preliminary washing of the slag containing the aluminum oxide from the salts by its treatment with the sulfuric acid, separation by filtering of the produced solution from the sand. The sand is flushed, and the purified solution after filtration is fed into the crystallizer tank and cooled. Separate the crystals of aluminum sulfate from the mother solution, which composition contains the sulfuric acid. T the crystals of aluminum sulfate are flushed by the organic solvent, dried and packed in the bags. After this flushing they separate the organic solvent at the temperature of its boiling point by distillation from the remained mixture of the organic solvent, the water and the sulfuric acid. The liquefied organic solvent is used in the subsequent flushing operations, and the mother solution, which contains the sulfuric acid, is used on the subsequent stages of the slag treatment. The invention allows to realize effectively the universal wasteless ecologically safe technology of production of aluminum sulfate.
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Method for preparing modified aluminum sulfate / 2291108
Invention relates to technology of inorganic substances, in particular, to a method for preparing aluminum sulfate-base coagulant used in processes of water preparing and treatment of sewage of different origin. Method for preparing modified aluminum sulfate involves feeding sulfuric acid to aluminum hydroxide suspension with heating the reaction mixture, addition of a primer, keeping the reaction mixture at temperature 105-120°C and the following crystallization of a prepared melt. After feeding all amount of sulfuric acid to the reaction mixture a primer is added as carbon aqueous suspension of fraction less 0.5 mm and in the ratio solid : liquid = 1:(2.0-4.0) wherein the amount of added carbon in the modified aluminum sulfate is 2-5 weight%. Invention provides preparing modified aluminum sulfate in a solid state that possesses the enhanced coagulating capacity.
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Method of production of rare-earth element fluorosulphide powders / 2500502
Invention relates to inorganic chemistry, particularly to production of powders to be used in laser technology and optical instrument making. Proposed method comprises preparation of blend and its thermal treatment. Said blend is prepared from the powder of sesquialteral rare-earth element sulphides with particle size of 1-30 mcm and powder of rare-earth element trifluorides with particle size of 10-70 nm at molar ratio of 1:1.Thermal treatment of the blend is conducted at 650-800 °C for 20-30 minutes in atmosphere of argon, sulfiding gases H2S+CS2 and fluoridiser gases C2F4, CF4 obtained in Teflon pyrolysis.
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Method of obtaining complex scandium chloride and alkali metal / 2497755
Invention relates to inorganic chemistry and deals with method of obtaining complex scandium chloride and alkali metal. Metallic scandium is mixed with lead dichloride and salt of alkali metal. Obtained charge is placed into crucible with inert atmosphere, heated to reaction temperature in presence of metallic lead and kept at temperature, exceeding melting temperature of mixture of salts by 50-100°, for 10-30 minutes. Metallic scandium is applied in compact form in from of pieces. As salt of alkali metal, metals chlorides are applied. In initial charge mixture of chloride salts of alkali metals is applied.
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Method of producing powder of solid solutions of lanthanum, neodymium, praseodymium and samarium oxysulphides / 2496718
Invention relates to inorganic chemistry and specifically to a method of producing powder of solid solutions of rare-earth oxysulphides for making ceramic articles, phosphors and laser materials. The method of producing powder of solid solutions of lanthanum, neodymium, praseodymium and samarium oxysulphides involves preparing a mixture of given mass of weighted forms of rare-earth oxides dissolved in nitric acid, precipitating rare-earth sulphates from the obtained solution using concentrated sulphuric acid, evaporating the formed suspension on air at 70 - 90°C to a dry state, grinding and calcining at 600°C for 1.5 hours, further grinding to a fine state and treating in a hydrogen stream with gas feed rate of 6 eq/h with respect to the weight of rare-earth sulphates at the following temperatures and duration of heat treatment: 600°C - 10 hours, 700°C - 5 hours and 850°C - 1 hour.
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Molybdate-based inorganic pigment / 2492198
Invention can be used in paint-and-varnish industry, in making plastic, ceramics and construction materials. The molybdate-based pigment, which contains cerium and an alkali-earth metal, is a complex molybdate with a scheelite structure of the composition Ca1-3/2XCexMoO4, where 0.10≥x≥0.02.
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Method for synthesis of cuprates of barium and rare-earth elements / 2489356
Invention can be used in chemical industry. The method involves calcining a heteropolynuclear complex of nitrates of rare-earth elements, copper (II), barium and quinoline, after preliminary calcining, cooling and homogenisation. Basic calcining is carried out at temperature of 850°C for the yttrium subgroup, and at 750°C for the cerium subgroup.
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Synthesis of cerium oxide nanoparticles in supercritical water / 2488560
Invention can be used in chemical industry. Cerium oxide CeO2 nanoparticles are obtained by mixing 0.2 M Ce(NO3)3 · 6H2O solution with supercritical water. The reaction is carried out at temperature of 370-390°C and pressure of 240-260 atm. The ratio of the volume of the cerium salt solution to the volume of supercritical water is preferably equal to 2:10.
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Method of extracting rare-earth metals from phosphogypsum / 2487834
Invention can be used in chemical industry and production of construction materials. Proposed method comprises processing phosphogypsum by sulfuric solution, filtration, extraction of precipitate of rare-earth metal insoluble compounds and separation of precipitate by filtration. Rare-earth metals are extracted from solution by oxalic acid or its soluble salts at consumption of 250-300 mol % while solution is neutralised to pH=1.0-2.5. Obtained precipitate of oxalates is separated from mother solution, rinsed, dried and calcined.
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Fuel additive containing cerium dioxide nanoparticles with altered structure / 2487753
Invention relates to a method of producing cerium dioxide nanoparticles and use thereof. Described is a method of producing cerium dioxide nanoparticles with a given lattice, which contain at least one transition metal (M), wherein: (a) an aqueous reaction mixture is prepared, said mixture containing a source of Ce3+ ions, a source of ions of one or more transition metals (M), a source of hydroxide ions, at least one nanoparticle stabiliser and an oxidant which oxidises the Ce3+ ion to a Ce4+ ion, at initial temperature ranging from about 20°C to about 95°C; (b) mechanical shearing of said mixture and passing said mixture through a perforated sieve to form a homogeneously distributed suspension of cerium hydroxide nanoparticles; and (c) creating temperature conditions that are effective for oxidation of the Ce3+ ion to a Ce4+ ion to form a product stream containing cerium dioxide nanoparticles, containing a transition metal Ce1-xMxO2, where x assumes a value from about 0.3 to about 0.8, said nanoparticles have a cubic fluorite structure, average hydrodynamic diameter ranging from about 1 nm to about 10 nm and geometric diameter from about 1 nm to about 4 nm, wherein the nanoparticle stabiliser is water-soluble and has a value Log KBC ranging from 1 to 14, where KBC denotes a constant for binding the nanoparticle stabiliser to a cerium ion in water and said temperature conditions that are effective for oxidation of the Ce3+ ion to a Ce4+ ion include temperature from about 50°C to about 100°C. Described is a method of preparing a homogeneous dispersion containing stabilised crystalline nanoparticles of cerium dioxide with a given lattice, containing a transition metal, Ce1-xMxO2, where M is at least one transition metal and x assumes a value from about 0.3 to about 0.8; (a) preparing an aqueous mixture which contains stabilised cerium dioxide nanoparticles containing a transition metal, Ce1-xMxO2, having a cubic fluorite structure, wherein, wherein said nanoparticles have average hydrodynamic diameter ranging from about 1 nm to about 10 nm and geometric diameter less than about 4 nm; (b) concentrating said aqueous mixture containing said stabilised cerium dioxide nanoparticles containing a transition metal, thereby forming an aqueous concentrate; (c) removing essentially all water from said aqueous concentrate to form an essentially water-free concentrate of stabilised cerium dioxide nanoparticles containing a transition metal; (d) adding an organic diluent to said essentially water-free concentrate to form an organic concentrate of said stabilised cerium dioxide nanoparticles containing a transition metal; and (e) merging said organic concentrate with a surfactant in the presence of a nonpolar medium to form said homogeneous dispersion containing stabilised crystalline nanoparticles of cerium dioxide containing a transition metal, Ce1-xMxO2, where M and x assume values given above. Described is a deposited coating for the catalytic converter of the exhaust system of an internal combustion engine, where said deposited coating is obtained using said homogeneous dispersion.
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Method of processing phosphogypsum / 2487083
Method of processing phosphogypsum involves leaching phosphogypsum which contains rare-earth elements and impurities, including phosphorus, fluorine and sodium, by passing sulphuric acid solution with concentration of 3-6 wt % at liquid-to-solid ratio of 1.5-2.0 through a layer of phosphogypsum to transfer the rare-earth elements and impurity components into the leaching solution. The leaching solution is separated in form of two consecutive portions, the volume of the first portion being smaller. The first portion is neutralised with a calcium-containing reagent to pH 6-8 and the precipitate which contains impurity components is separated. The calcium-containing reagent used is slaked or unslaked lime. The second portion of the leaching solution is taken for sorption extraction of rare-earth elements using a sulphoxide cationite to obtain a lean sulphuric acid solution. After leaching, the phosphogypsum is washed with water in amount of 0.4-0.5 l per kg of phosphogypsum to obtain washed phosphogypsum and washing sulphuric acid solution. That solution is mixed with the lean sulphuric acid solution, fortified with strong acid and taken for leaching phosphogypsum.
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Method of producing dieuropium oxide-diiodide eu2oi2 / 2485050
Invention relates to production of binary compounds, specifically europium (II) oxoiodides, which are used as components of luminescent materials and also a method of producing dieuropium oxide-diiodide Eu2OI2. Reagents are added to the starting europium iodide derivative, followed by heating the mixture, holding at high temperature and then cooling to room temperature; the starting europium iodide derivative used is a nanohydrate of europium (III) iodide, the reagent used is thiocarbamide and the weight ratio of the starting europium iodide derivative to the reagent is equal to (5.10-5.30):1; the mixture is heated at a rate of 8-12 deg/min to temperature of 270-320°C, followed by holding for 1-2 hours and further cooling to room temperature at a rate of 3-5 deg/min.
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Composite filter from porous block with nanofibres / 2502543
Invention relates to composite composed of porous block with nanofibres. Porous block has one pore or multiple pores and multiple inorganic nanofibres grown inside block pores in hydrothermal process. Inorganic fibers are produced from aluminate, titanate or inorganic oxide. Said porous block is composed of one of the following materials: carbon, metal oxide, silicon, cellulose and organic polymer. Invention covers also the method of making said composite and filter incorporating it.
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FIELD: process engineering.
SUBSTANCE: invention relates to processing of wastes, particularly, to ash-and-slag wastes of thermal electric power stations. Coal combustion ash is placed in reaction zone to add carbon sorbent thereto in amount of 10-25 kg per ton of ash. Then, it is processed by the mix of ammonium fluoride and sulfuric acid, heated to 120-125°C and held thereat for 30-40 minutes. Tetrafluorosilane resulted from said processing is absorbed by ammonium fluoride. Solution of ammonium hydroxide is introduced into that of ammonium tetrafluorosilicate to precipitation of silicon dioxide. Then, concentrated sulfuric acid in double surplus is added to aluminium residue, held at 250°C for 1.5 h and processed by water. Solid residue is calcined at 800°C.
EFFECT: production of highly-dispersed silicon dioxide, aluminium sulphate, concentrate of rare and rare-earth elements.
2 cl, 6 tbl, 2 ex
The invention relates to the field of processing silicon-containing raw materials, including ash waste CHP plants with the aim of obtaining a number of products: highly dispersed silicon dioxide, aluminium sulphate, concentrate of rare and rare earth elements.
It is known that at the present time to obtain highly dispersed silicon dioxide is used treatment of river sand calcium fluoride with 75-80% sulfuric acid [Rakov EG, Teslenko V.V. Pyrohydrolysis of inorganic fluorides. M - Energoatomizdat, 1987 - 151 C.]. The processing of sand calcium fluoride and sulfuric acid is carried out in rotary kilns at a temperature of 200-250°C. the Disadvantages of this method is the necessity of using sulfuric acid of high concentration and clean river sand.
There is a method for processing man-made and natural siliceous raw materials to produce silicon dioxide by treatment with solutions of hydrofluoric acid [Leaching with hydrofluoric acid aluminosilicate raw materials to produce cetarehhloristam silicon, aluminum fluoride, and fluorides and oxides of accompanying metals - US patent No. 5242670, IPC SW 033/08, No. 907854 from 02.07.92., publ. 7.09.93.]. The method consists in that the aluminosilicate raw materials are treated with a concentrated solution of HF. Released gaseous tetrafluorosilane (SiF4) is skipped is via a series of cooling traps, which remains a large part of the impurities. The cleaned gas is in contact with an aqueous solution of sodium fluoride, with formation of a suspension of fertilitate sodium (Na2SiF6), from suspension of isolated crystals fertilitate sodium on the filter media, after which they are dried, and then calcined at 600-650°C. the Gas tetrafluorosilane released during the calcination condense, receiving liquid net tetrafluorosilane. At the same time in the residue from the calcination get powdered sodium fluoride (NaF). The suspension remaining after the decomposition of the raw materials and the distillation of tetrafluorosilane and containing aluminum fluoride and a small amount of secondary metal salts, dilute with water going into the liquid phase soluble salts. The resulting solution is separated from the insoluble residue. After evaporation receive the remainder trihydrate aluminum fluoride mixed with salts of related metals contained in the feedstock. After evaporation of the solution emitted gaseous Forestwood (HF) condense and return to the cycle. Equation flowing reactions:
SiO2+4HF→SiF4↑+2H2O
2NaF+SiF4→Na2SiF6↓
Na2SiF6→2NaF+SiF4↑
The disadvantage of this method is the use of 50%hydrofluoric acid which is the substance of the first class of danger that makes the proposed technology environmental the ski threat.
A method of refining aluminum silicates on the aluminum fluoride which is processed ash Ekibastuz coal [inventor's certificate SU # 1668301, MKI C01F 7/50, application No. 4671911 from 03.04.89, publ. 07.08.91 - Way processing of silicates on the aluminum fluoride. / L.D. Shapiro, V.I. Shapoval, Mac, S.O. Akhmetov, VA, Gubenko]. Ash from the combustion of high-ash coal calcined at 550-750°C in a closed reactor, and then subjected to magnetic separation. The non-magnetic fraction is treated with ammonium fluoride in the amount of 100-120% of the stoichiometrically required for the formation of aluminum fluoride and crematoria ammonium at 300-600°C. the Resulting gases tetrafluorosilane, ammonia (NH3), water and hydrogen fluoride is distilled off and absorb in the sink with water, to obtain silica and ammonium fluoride (NH4F). Silicon dioxide is filtered off and the remaining solution evaporated. Eye-catching ammonium fluoride return in the cycle. The resulting spectra, containing up to 90% of aluminum fluoride, can be used in the aluminum industry. Further use of the resulting hydrolysis of silicon dioxide is not considered [Copyright certificate №1668301, USSR C01F 7/50].
Equation flowing reactions:
SiO2+4NH4F→4NH3↑+SiF4↑+2H2About
SiO2+6NH4F→(NH4)2SiF6+4NH ↑+2H2O
NH4F→NH3↑+HF↑
The disadvantage of this method is the use of high temperature, as well as getting tetrafluorosilane contaminated with ammonia, which necessitates the stage of separation and utilization of ammonia by absorption of water. Also not considered further use of the solid residue after fluorination ash.
Closest to the claimed method is hydrochemical obtain highly dispersed silicon dioxide from man-made materials [Patent RU No. 2261841, application No. 2004109475 from 29.03.04, publ. 10.10.05 - Barbat VF and others].
In this way as a fluorinating agent used calcium fluoride and sulfuric acid, or industrial wastes containing fluoride and sulfuric acid. In the method of fluoridation ash produce hydrogen fluoride, directly emitted in the reaction zone. Run reaction:
The reaction of sulfuric acid with an inorganic fluoride in a Teflon reactor produces hydrogen fluoride (1), which interacts with components of the ash, forming various fluoride and gaseous tetrafluorosilane (2). Tetrafluorosilane absorb 15%solution of ammonium fluoride (3) 3-the series-connected polypropylene sinks. Then pour the resulting solution from the absorber and neutralize 20%ammonia solution (4). It stands a highly dispersed silicon dioxide, which is filtered off. In the present method chetyrehhloristy silane is not contaminated with ammonia, which is an advantage of the method. The disadvantage of this method is the fact that it discusses the possibility of obtaining from the ashes only highly dispersed silica, but contained in large quantities in the ashes aluminum and expensive rare metals remain in the solid products after fluorination and not disposed of. The use of calcium fluoride or industrial waste will lead to difficulties in further processing of the solid products of the fluorination ash from contaminated gypsum and other products, in the case of man-made waste.
The present invention is to develop a method for integrated processing of ash from burning coal to use as a fluorinating agent of a mixture of ammonium fluoride and sulfuric acid, in the reaction zone additionally injected carbon sorbent. To achieve the specified result, it is proposed to use a mixture of ammonium fluoride, sulfuric acid, silicon-containing wastes of industry and energy - ash CHP as ash contains up to 60% silicon dioxide, which can be seen from hee the systematic composition of ash on the primary (% mass.) and microcomponents (grams/tonne) components, presented in tables 1 and 2, and the process is carried out at a temperature of 120±5°C.
Table 1 |
SiO2 |
Al2O3 |
Fe2O3 |
CaO |
MgO |
TiO2 |
K2O |
Na2O |
P2O5 |
MnO2 |
SO3 |
SPT |
61,5 |
27,4 |
the 5.65 |
1,17 |
0,49 |
1,49 |
0,42 |
0,32 |
0,52 |
0,17 |
0,57 |
5,1 |
Table 2 |
Sr |
Ba |
Y |
La |
CE |
Yb |
Tb |
Dy |
|
Th |
U |
Zr |
Cu |
V |
Ga |
Sc |
420 |
200 |
42 |
15 |
67 |
6 |
9 |
10 |
7 |
2 |
330 |
57 |
140 |
43 |
90 |
To obtain a concentrate containing rare and rare - earth elements, Sc, Y, Ce, La, Ga, when fluoridation of ash in the reactor in the fluorination impose additional carbon sorption material in a quantity sufficient for sorption of rare and rare earth elements. Rare and rare-earth elements partially remain in the form of fluorides, and in part will focus on the carbon sorbent, resulting in total can be allocated in the form of a concentrate.
In the proposed method the sample of ash from coal combustion, for example Ekibastuz, placed in a Teflon reactor, add carbon sorbent in the amount of 10-25 kg per ton of ash, which is 1-2,5% by weight of the s ash. The consumption of carbon sorbent is less than 1% leads to a decrease in REE content in the solid residue to 0.6%, and increase the flow of carbon sorbent more than 2.5% does not increase the content of REE in the resulting solid residue. Then the sample is mixed with ammonium fluoride at a mass ratio of the silica in the ash content of the fluoride ammonium fluoride 1:1, poured 50-55%sulfuric acid, heated to 120-125°C and incubated for 30-40 minutes, simultaneously driving the formed tetrafluorosilane in the sink filled with a solution of ammonium fluoride using a vacuum pump.
The reaction of sulfuric acid with ammonium fluoride in a Teflon reactor produces hydrogen fluoride, which interacts with components of the ash, forming various fluoride and gaseous tetrafluorosilane. Tetrafluorosilane absorb 15%solution of ammonium fluoride in 3 series-connected polypropylene sinks. Then pour the resulting solution from the absorber and neutralize 20%ammonia solution. It stands a highly dispersed silicon dioxide, which is filtered off.
The solution after filtration of silicon dioxide evaporated, receiving ammonium fluoride, is returned to the absorption of tetrafluorosilane. Table 3 presents the dependence of the yield of silicon dioxide from an excess of the estimated Koli is esta fluorine in the ammonium fluoride and sulfuric acid at a temperature of 120°C.
Table 3 |
An excess of H2SO4 |
Excess fluoride |
The output of silicon dioxide, % |
1:1 |
1:1 |
21,0 |
1:2 |
1:1 |
54,0 |
1:3 |
1:1 |
90,0 |
The table shows that at a temperature of 120°C, 3-fold excess of 50%sulfuric acid and the consumption of fluoride in the fluoride ammonium 1:1 extracts up to 90% of silicon dioxide. The output calculation is conducted on the original silicon dioxide content in the ash. The excess of sulfuric acid or ammonium fluoride are presented as the ratio of the amounts of ammonium fluoride or sulfuric acid required for complete interaction of macro-ash (aluminum oxide, silicon oxide) contained in the sample, calculated theoretically by reactions 5, 6, 7 to the amount of substance of ammonium fluoride or sulfuric acid added in the experiment.
5. 2NH4F+H2SO4=(NH4)2SO4+2HF
6. SiO2+4HF=SiF4+2H2About
7. Al2O3+6HF=2AlF3+3H 2About
The greater the excess of sulphuric acid does not lead to a significant increase in the extraction of silicon from the ashes. So when a 4-fold excess of the degree of extraction of silicon increases to 92%, which makes this an excess of sulfuric acid is not appropriate.
Tetrafluorosilane distilled and processed on silicon dioxide as in method [Patent RU No. 2261841, application No. 2004109475 from 29.03.04, publ. 10.10.05 - Barbat VF and others]. And the remainder is processed with the purpose of selection of aluminum sulfate and concentrate of rare and rare earth elements. To do this, the obtained solid product fluoridation translate the aluminum fluoride in soluble form by adding a 2-fold excess of concentrated sulfuric acid and heating to a temperature of 250°C for 1.5 hours. Data on the extraction of aluminum sulfate in the solution from the consumption of acid is at a temperature of 120°C. and processing time of 30 minutes is shown in table 4.
Table 4 |
The ratio of T:W (solid residue: sulfuric acid) |
The degree of extraction of aluminum sulfate, % |
1:1 |
32,6±1,8 |
1:2 |
51,5±2,6 |
1:3 |
54,5±2,8 |
|
From table 4 it follows that you should take a 2-fold excess of sulfuric acid. High consumption of acid does not significantly increase the degree of extraction of aluminum sulfate from the solid residue fluoridation. Data on the dependence of the degree of extraction of aluminum sulfate in solution temperature and processing time in a double excess of concentrated sulfuric acid are given in table 5.
Table 5 |
Processing time |
120°C |
250°C |
α(Al2(SO4)3), % |
α(Al2(SO4)3), % |
0 |
0 |
0 |
10 |
20,1±1,0 |
28,0±1,4 |
20 |
36,9±1,8 |
51,6±2,6 |
30 |
51,5±2,6 |
64,8±3,2 |
50 |
60,0±3,0 |
78,3±3,9 |
70 |
66,4±3,3 |
at 88.1±4,4 |
90 |
70,2±3,5 |
92,0±4,6 |
Further increase in temperature is not advisable because of the high corrosivity of the reaction mixture. In the processing of solid products of fluorination of concentrated sulfuric acid in the above conditions, the aluminum fluoride enters sulfate. After cooling, the reaction mixture is treated with water when aluminum sulfate is dissolved, the remaining precipitate was separated by filtration and calcined. The solid product after calcination is a concentrate of rare and rare earth elements.
To eliminate contamination of the product aluminium by iron, it is recommended to conduct magnetic separation of ash for disposal of ash valuable product - magnetospheres [Anshits A.G. Selection of magnetic microspheres permanent part of the energy is evil, and the study of their physico-chemical properties // chemistry for sustainable development, 1999. - VIP. - s-118].
The results can be illustrated by the following examples.
Example 1: 59,7 g ash from the combustion of coal from Ekibastuz (selected fields 1-4 electrostatic CHP-4 Omsk) mix with is 129.3 g of ammonium fluoride (PM). Placed in a Teflon reactor (1), add 1.5 g of carbon sorbent BAU added 518 ml 50-55-Oh sulphuric acid, heated to 120°C and maintained at this temperature for 30 minutes, at the same time fending off the released gaseous tetrafluorosilane. Absorbed it with a 15%solution of ammonium fluoride in polypropylene sinks (2). The resulting solution of ammonium fluorosilicate preparation (NH4)2SiF6pour into a polypropylene beaker and to it there is added a 20%solution of ammonia until the smell of ammonia.
Precipitated silica is filtered and dry at a temperature of 110 OC. The degree of extraction of tetrafluorosilane is 92%. The residue after distillation of tetrafluorosilane contains up to 75% of aluminum TRIFLUORIDE, up to 2% silicon dioxide. Else, sulfuric acid, nadareh contained in the original ash, fluoride, iron and REE. The specific surface of the obtained silicon dioxide determined by BET method is 400±15 m2/year
To the residue is poured 120 ml of concentrated sulfuric acid, heated to 250 for 1.5 hours, cooled, treated with water (800 ml), the precipitate filtered off. The solution is extracted 95% of the aluminum contained in the original ash.
Filtered the solid residue calcined at 800°C. the Mass of the solid residue is 2% by weight of the original ash, the composition of the residue is analyzed by the spectrophotometric method semi-quantitative atomic-emission analysis. Data on the chemical composition of the residue after Prokaeva the Oia in % are given in table 6.
Table 6 |
Si |
Fe |
Al |
REE |
VA |
Mn |
Zr |
Hf |
Co |
Ni |
V |
Sr |
10-100 |
~1 |
~1 |
~1 |
~0,2 |
~0,2 |
~0,2 |
~0,06 |
~0,02 |
~0,02 |
~0,02 |
~0,02 |
This method allows you to expand the raw material base to obtain highly dispersed silicon dioxide due to the use of angry CHP
Example 2. Ash from burning coal is treated in the same conditions as in example 1, but additionally introduce nanostructured carbon sorbent derived IPPO SB RAS (Omsk). Removing the silicon and aluminum remains the same as in example 1. The REE content in the solid residue is 1.3%.
1. The method of complex overtime and ash from coal burning, in which the ash from burning coal is placed in a reaction zone, add carbon sorbent, providing absorption of rare and rare earth elements, in the amount of 10-25 kg per ton of ash, then treated with a mixture of ammonium fluoride and sulfuric acid, heated to 120-125°C, incubated for 30-40 min, the resulting tetrafluorosilane absorb ammonium fluoride and the resulting solution tetraberlinia ammonium enter solution of ammonium hydroxide prior to the deposition of silicon dioxide, then add concentrated sulfuric acid in a two-fold excess contained in the remainder aluminum, maintained at a temperature of 250°C for 1.5 h and treated water, the solid residue is filtered and calcined at 800°C.
2. The method according to claim 1, characterized in that from the ashes previously removed iron magnetic separation.
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