CN110467222B - Method for preparing vanadium pentoxide - Google Patents
Method for preparing vanadium pentoxide Download PDFInfo
- Publication number
- CN110467222B CN110467222B CN201910843176.6A CN201910843176A CN110467222B CN 110467222 B CN110467222 B CN 110467222B CN 201910843176 A CN201910843176 A CN 201910843176A CN 110467222 B CN110467222 B CN 110467222B
- Authority
- CN
- China
- Prior art keywords
- solution
- vanadium pentoxide
- ammonium
- vanadium
- temperature
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Active
Links
- GNTDGMZSJNCJKK-UHFFFAOYSA-N divanadium pentaoxide Chemical compound O=[V](=O)O[V](=O)=O GNTDGMZSJNCJKK-UHFFFAOYSA-N 0.000 title claims abstract description 76
- 238000000034 method Methods 0.000 title claims abstract description 24
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid Substances OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 30
- UNTBPXHCXVWYOI-UHFFFAOYSA-O azanium;oxido(dioxo)vanadium Chemical compound [NH4+].[O-][V](=O)=O UNTBPXHCXVWYOI-UHFFFAOYSA-O 0.000 claims abstract description 23
- 238000002386 leaching Methods 0.000 claims abstract description 20
- 238000004519 manufacturing process Methods 0.000 claims abstract description 19
- 239000000376 reactant Substances 0.000 claims abstract description 19
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000007791 liquid phase Substances 0.000 claims abstract description 17
- 238000000926 separation method Methods 0.000 claims abstract description 15
- 238000006243 chemical reaction Methods 0.000 claims abstract description 14
- 238000005342 ion exchange Methods 0.000 claims abstract description 14
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims abstract description 13
- 235000011130 ammonium sulphate Nutrition 0.000 claims abstract description 13
- 238000003756 stirring Methods 0.000 claims abstract description 13
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 12
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims abstract description 9
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 claims abstract description 9
- 235000012538 ammonium bicarbonate Nutrition 0.000 claims abstract description 9
- 239000001099 ammonium carbonate Substances 0.000 claims abstract description 9
- 239000007788 liquid Substances 0.000 claims abstract description 9
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 claims abstract description 8
- 238000000354 decomposition reaction Methods 0.000 claims abstract description 8
- 239000007790 solid phase Substances 0.000 claims abstract description 8
- 239000003480 eluent Substances 0.000 claims abstract description 5
- 229910001629 magnesium chloride Inorganic materials 0.000 claims abstract description 4
- 239000007800 oxidant agent Substances 0.000 claims abstract description 4
- 230000003647 oxidation Effects 0.000 claims abstract description 4
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 4
- 230000001590 oxidative effect Effects 0.000 claims abstract description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 43
- 229910001868 water Inorganic materials 0.000 claims description 43
- 229910052720 vanadium Inorganic materials 0.000 claims description 31
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 claims description 31
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 18
- 239000003245 coal Substances 0.000 claims description 12
- 239000004575 stone Substances 0.000 claims description 12
- 238000001354 calcination Methods 0.000 claims description 9
- 238000007872 degassing Methods 0.000 claims description 9
- 239000000843 powder Substances 0.000 claims description 9
- 238000001556 precipitation Methods 0.000 claims description 9
- -1 ammonium ions Chemical class 0.000 claims description 8
- 238000000227 grinding Methods 0.000 claims description 8
- 239000012528 membrane Substances 0.000 claims description 8
- 238000001238 wet grinding Methods 0.000 claims description 7
- 235000011124 aluminium ammonium sulphate Nutrition 0.000 claims description 6
- LCQXXBOSCBRNNT-UHFFFAOYSA-K ammonium aluminium sulfate Chemical compound [NH4+].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O LCQXXBOSCBRNNT-UHFFFAOYSA-K 0.000 claims description 6
- 239000012452 mother liquor Substances 0.000 claims description 6
- MCPTUMJSKDUTAQ-UHFFFAOYSA-N vanadium;hydrate Chemical compound O.[V] MCPTUMJSKDUTAQ-UHFFFAOYSA-N 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 5
- 229910052782 aluminium Inorganic materials 0.000 claims description 5
- 239000000919 ceramic Substances 0.000 claims description 5
- 238000005485 electric heating Methods 0.000 claims description 5
- 238000004064 recycling Methods 0.000 claims description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 3
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 3
- 239000000292 calcium oxide Substances 0.000 claims description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 3
- 239000013078 crystal Substances 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- 230000035484 reaction time Effects 0.000 claims description 3
- 239000000243 solution Substances 0.000 description 39
- 239000007789 gas Substances 0.000 description 5
- 239000012510 hollow fiber Substances 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 4
- 230000008929 regeneration Effects 0.000 description 4
- 238000011069 regeneration method Methods 0.000 description 4
- 229910021529 ammonia Inorganic materials 0.000 description 3
- 239000003054 catalyst Substances 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 239000010413 mother solution Substances 0.000 description 3
- 239000002912 waste gas Substances 0.000 description 3
- HSEYYGFJBLWFGD-UHFFFAOYSA-N 4-methylsulfanyl-2-[(2-methylsulfanylpyridine-3-carbonyl)amino]butanoic acid Chemical compound CSCCC(C(O)=O)NC(=O)C1=CC=CN=C1SC HSEYYGFJBLWFGD-UHFFFAOYSA-N 0.000 description 2
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 125000004122 cyclic group Chemical group 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 239000012071 phase Substances 0.000 description 2
- 235000021110 pickles Nutrition 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- 229910000628 Ferrovanadium Inorganic materials 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910000329 aluminium sulfate Inorganic materials 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 235000019270 ammonium chloride Nutrition 0.000 description 1
- 150000001450 anions Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 238000003889 chemical engineering Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 238000010924 continuous production Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000009615 deamination Effects 0.000 description 1
- 238000006481 deamination reaction Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000007791 dehumidification Methods 0.000 description 1
- 210000003298 dental enamel Anatomy 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000003837 high-temperature calcination Methods 0.000 description 1
- 238000000338 in vitro Methods 0.000 description 1
- 238000001727 in vivo Methods 0.000 description 1
- PNXOJQQRXBVKEX-UHFFFAOYSA-N iron vanadium Chemical compound [V].[Fe] PNXOJQQRXBVKEX-UHFFFAOYSA-N 0.000 description 1
- 239000000696 magnetic material Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 238000005272 metallurgy Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 230000005070 ripening Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000011895 specific detection Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01G—COMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
- C01G31/00—Compounds of vanadium
- C01G31/02—Oxides
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Inorganic Compounds Of Heavy Metals (AREA)
Abstract
A method for preparing vanadium pentoxide belongs to the field of vanadium pentoxide production, and comprises the following steps: (A) pouring the ore pulp into a reaction kettle, stirring along the middle to form a pit, pouring concentrated sulfuric acid into the pit, uniformly stirring, and curing at constant temperature to obtain a first reactant; (B) the first reactant is subjected to multi-stage countercurrent leaching separation to obtain a solid phase and a liquid phase; (C) adding ammonium bicarbonate into the liquid phase, and performing solid-liquid separation to obtain a first solution; (D) adding an oxidant into the first solution for oxidation, carrying out ion exchange enrichment on the first solution to obtain a second solution, and eluting the second solution by using a sodium hydroxide solution to obtain an eluent; (E) adding a magnesium chloride solution into the eluent to obtain a third solution; (F) and adding ammonium sulfate into the third solution, performing centrifugal separation to obtain ammonium metavanadate, and finally performing decomposition reaction on the ammonium metavanadate to obtain vanadium pentoxide.
Description
Technical Field
The invention relates to the field of vanadium pentoxide production, in particular to a method for preparing vanadium pentoxide.
Background
Vanadium is a non-ferrous metal, and vanadium pentoxide is widely used in the industries of metallurgy, chemical industry and the like, and is mainly used for smelting ferrovanadium. The catalyst is used as an alloy additive and accounts for more than 80 percent of the total consumption of vanadium pentoxide, is used as a catalyst of organic chemical engineering, namely a catalyst, and accounts for about 10 percent of the total amount, and is used as an inorganic chemical, a chemical reagent, enamel, a magnetic material and the like in other places, and accounts for about 10 percent of the total amount.
At present, two methods for extracting vanadium pentoxide from stone coal by using sulfuric acid are mainly used, one method is a dilute acid heating extraction method, the production period of the method is long, 9-12 hours are needed, the energy consumption is high, and the impurities in an extracting solution are more; the other method is a solid mineral powder mixed concentrated acid heap leaching method, the method has longer period, needs at least 5-7 days, occupies large production area, and has severe production environment and great pollution.
For example, application numbers are: CN201410520118.7 discloses a method for preparing vanadium pentoxide, which comprises crushing and grinding dry stone coal with low water content to 80 meshes, mixing with concentrated sulfuric acid and water in a certain proportion, and directly heap leaching in open air. Fermenting at constant temperature for 7-10 days, adding water, leaching, and performing solid-liquid separation. Obtaining pickle liquor containing vanadium. Adding ammonium bicarbonate into the vanadium-containing pickle liquor to prepare ammonium alum, and removing aluminum. Then the separation liquid is subjected to ion exchange to enrich vanadium in the solution. After being eluted by alkali liquor, the ammonium metavanadate is prepared by removing impurities and adding ammonium chloride or ammonium sulfate, and finally vanadium pentoxide is obtained by high-temperature calcination.
Disclosure of Invention
The technical problem to be solved by the invention is as follows: overcomes the defects of the prior art, and provides the method for preparing the vanadium pentoxide, which can eliminate dust pollution, reduce the production cost and has short production period.
The technical scheme adopted by the invention for solving the technical problems is as follows: a method for preparing vanadium pentoxide comprises the following steps:
(A) grinding stone coal by a wet grinding ball mill, simultaneously controlling the water addition amount to obtain ore pulp containing 30-40% of water, pouring the ore pulp into a reaction kettle, stirring along the middle to form a pit, pouring concentrated sulfuric acid into the pit, uniformly stirring, and curing at constant temperature for 4-6 h to obtain a first reactant;
(B) carrying out multi-stage countercurrent leaching separation on the first reactant at normal temperature to obtain a solid phase and a liquid phase, wherein the solid phase is ore tailings with the water content of less than 20% by mass, and the liquid phase is a vanadium-containing acid solution;
(C) adding a certain amount of ammonium bicarbonate or ammonium sulfate into the liquid phase, and performing solid-liquid separation to obtain ammonium alum crystals and a first solution;
(D) adjusting the pH value of the first solution to 2.0-2.5, adding an oxidant for oxidation, and performing ion exchange enrichment to obtain a vanadium-containing barren solution and a second solution, wherein the second solution is an eluent obtained by eluting with a sodium hydroxide solution;
(E) adjusting the pH value of the second solution to 8.5-9.5, and adding the second solution in a mass ratio of 1: reacting 0.12 of 20% magnesium chloride solution at the temperature of 80-100 ℃ for 2 hours, and filtering to obtain a third solution;
(F) adding vanadium to ammonium in a molar ratio of 1: 1.2, stirring and reacting for 2 hours at the temperature of 40-60 ℃, centrifugally separating to obtain ammonium metavanadate and vanadium precipitation mother liquor, and finally, carrying out decomposition reaction on the ammonium metavanadate to obtain vanadium pentoxide.
The method is between two methods in the prior art, concentrated sulfuric acid and ore pulp are cured in a reaction kettle, the curing time is short, wet grinding is adopted, and the concentrated sulfuric acid and the ore pulp are cured in the reaction kettle, so that no dust is generated; the ore pulp is stirred to form a pit at the center of the ore pulp, and the pit is used for pouring concentrated sulfuric acid, so that the concentrated sulfuric acid cannot be sputtered when being added, and the mixing of the concentrated sulfuric acid and the ore pulp can be accelerated; multistage countercurrent leaching refers to a process in which multistage leaching is carried out in a multistage series of equipment. Each stage includes a primary leaching chamber and a secondary leaching chamber. The solid phase is provided in the leaching chamber for contact with a leaching agent which is releached when in contact with the receiver in the releaching chamber. The leachant is suitably cross-flowed in the same stage to the donor and acceptor phases, with the donor and acceptor phases being counter-flowed through some or all of the stages, and multi-stage counter-current leaching is known in the art and will not be described in any greater detail herein.
The first solution, the second solution and the third solution are all vanadium-containing solutions, and the ion exchange equipment is an ion exchange column, which is a columnar pressure container for carrying out ion exchange reaction and is exchange equipment for ion exchange by a column method. Is often used in laboratories and industry. The method can be divided into three types of in-vivo regeneration mixed bed, in-vitro regeneration mixed bed and anion resin outward transfer regeneration mixed bed according to a regeneration mode, and can be divided into a laboratory ion exchange column and an industrial ion exchange column in the application range, wherein the ion exchange column can generate two solutions, one is a saturated second solution, the other is a vanadium-containing barren solution, the vanadium-containing barren solution contains a large amount of metal impurities, and the vanadium-containing barren solution can be returned to the step (A) for water use after further reaction.
Further, in the step (A), the stone coal is ground to be smaller than 100 meshes by a wet grinding ball mill, the grinding can reduce the curing time, and under the condition of a certain temperature, the curing time of the stone coal is shorter as the stone coal is smaller within a range smaller than 100 meshes, and when the stone coal is larger than 100 meshes, the curing time of the stone coal is certain and is not reduced as the stone coal becomes smaller.
Further, the ore pulp and concentrated sulfuric acid in the step (A) are cured for 5-6 hours at the temperature of 110-120 ℃ to obtain a first reactant.
Further, the ore pulp containing 30% -40% of water in the step (A) is processed through a ceramic filter to obtain 15% -20% of wet ore powder, the wet ore powder and concentrated sulfuric acid are cured for 4-5 hours at the temperature of 120-130 ℃ to obtain a first reactant, the ceramic filter is the prior art, redundant description is omitted, and the curing time of water in the ore pulp in the subsequent curing process can be further shortened.
Further, the molar ratio of ammonium ions in the ammonium bicarbonate or ammonium sulfate added in the step (C) to aluminum ions in the liquid phase is 1.2-1.5: 1, Al in liquid phase2(SO4)3Is easy to react with Na+,K+,NH4 +Plasma generates composite salt, so ammonium bicarbonate or ammonium sulfate is added into liquid phase, and the ammonium bicarbonate or ammonium sulfate can be mixed with Al2(SO4)3Reacting to generate aluminum ammonium sulfate, cooling and crystallizing the aluminum ammonium sulfate to obtain the ammonium alum, wherein the molecular formula of the ammonium alum is as follows: NH (NH)4Al(SO4)2·12H2O, so that the molar ratio of the added ammonium ions to the aluminum ions in the liquid phase is preferably 1.2-1.5: 1 ensures the reaction is complete.
And (3) further, adding calcium oxide into the vanadium-containing barren solution enriched by the ion exchange column in the step (D), adjusting the pH value to 6.0-7.0, returning to the multi-stage countercurrent leaching in the step (B) for recycling, wherein the cured first reactant is in a solid-liquid mixed viscous state, and the treated vanadium-containing barren solution can dilute the first reactant, promote partial dissolution and facilitate the multi-stage countercurrent leaching.
Further, after deamination is performed on the vanadium precipitation mother liquor obtained by centrifugal separation in the step (F) through a degassing membrane, returning to the ore grinding link in the step (A) for application, wherein the vanadium precipitation mother liquor is only water actually and contains a part of ammonia, and the ammonia in the vanadium precipitation mother liquor is removed through the degassing membrane and can be returned to the step (A) for use as water; the degassing membrane is a membrane separation product for removing gases in liquid, such as carbon dioxide, oxygen and ammonia nitrogen, by using the principle of diffusion. The degassing membrane contains a large number of hollow fibers, the walls of which have tiny pores through which water molecules cannot pass, but through which gas molecules can pass. When the degassing device works, water flows through the hollow fibers under certain pressure, and the gas is continuously pumped away from the outside of the hollow fibers under the action of the vacuum pump to form certain negative pressure, so that the gas in the water continuously overflows from the water through the hollow fibers, the aim of removing the gas in the water is fulfilled, and the degassing membrane is internally provided with a large number of hollow fibers so as to enlarge the area of a gas-liquid interface and accelerate the degassing speed.
Further, in the step (F), a calcination manner is adopted for decomposition reaction of ammonium metavanadate, the calcination temperature is 500-550 ℃, the reaction time is 2-3 hours, the ammonium metavanadate is decomposed to generate vanadium pentoxide, water and ammonia gas, and calcination of ammonium metavanadate to prepare vanadium pentoxide is prior art and is not described herein in detail.
Further, in the step (F), an electric heating mode is adopted for decomposition reaction of ammonium metavanadate, the ammonium metavanadate is decomposed to generate vanadium pentoxide, water and ammonia gas, and the preparation of the vanadium pentoxide by electric heating is more environment-friendly.
And (3) further, absorbing ammonia gas generated by decomposing the ammonium metavanadate with sulfuric acid to obtain ammonium sulfate salt, dissolving the ammonium sulfate salt, returning the dissolved ammonium sulfate salt to the step (F) to react with the third solution, and recycling the generated ammonia gas to prevent the generation of waste gas.
The invention has the beneficial effects that: according to the invention, the ore pulp with a certain water content is pumped into the reaction kettle, the center of the ore pulp is stirred to form a pit, concentrated sulfuric acid is added, and the pit is cured at a certain temperature under stirring, so that the whole production period is greatly shortened, the sealing operation is carried out, and the continuous production is realized; continuous multi-stage countercurrent leaching is adopted, the efficiency is high, the operation is convenient, the cost is reduced, the labor intensity is reduced, and the operation environment is greatly improved.
The lean solution containing vanadium and the vanadium precipitation mother solution generated by the method can be returned to a system for cyclic utilization after being treated, so that the whole method does not generate wastewater, and the environmental pollution is reduced; the ammonia gas generated by decomposing the ammonium metavanadate to prepare the vanadium pentoxide reacts with the sulfuric acid to obtain ammonium sulfate salt, and the ammonium sulfate salt can be returned to the system for cyclic utilization after being dissolved, so that the whole method does not generate waste gas, and the atmospheric pollution is reduced.
At present, the mining is generally carried out by adopting hole mining, mineral aggregates are wet aggregates with high water content, and the invention can directly carry out wet grinding by the wet aggregates without dehumidification, thereby reducing investment, eliminating dust pollution and lowering production cost; the ore pulp is cured in the reaction kettle to replace the original open-air heap leaching fermentation, so that the problems of large occupied area, long working time, environmental pollution and the like are solved, and the production cost is reduced.
Detailed Description
Embodiments of the present invention will be described in detail below with reference to examples, but it will be understood by those skilled in the art that the following examples are only illustrative of the present invention and should not be construed as limiting the scope of the present invention. The examples, in which specific conditions are not specified, were conducted under conventional conditions or conditions recommended by the manufacturer. The reagents or instruments used are not indicated by the manufacturer, and are all conventional products available commercially.
Example 1
The method for preparing vanadium pentoxide comprises the following steps:
step (A): grinding stone coal by a wet grinding ball mill to be smaller than 100 meshes, simultaneously controlling the water addition amount to obtain ore pulp containing 40% of water, pouring the ore pulp into a reaction kettle, stirring at the center to form a pit, adding concentrated sulfuric acid into the pit, uniformly stirring, curing at constant temperature for 6 hours, and obtaining a first reactant, wherein the temperature is 120 ℃;
step (B): carrying out multi-stage countercurrent leaching separation on the first reactant at normal temperature to obtain a solid phase and a liquid phase, wherein the solid phase is ore tailings with the water content of less than 20% by mass, and the liquid phase is a vanadium-containing acid solution;
step (C): adding a certain amount of ammonium bicarbonate or ammonium sulfate into the liquid phase, wherein the molar ratio of ammonium ions to aluminum ions in the liquid phase is 1.2-1.5: 1, obtaining ammonium alum crystals and a first solution through solid-liquid separation;
step (D): adjusting the pH value of the first solution to 2.0-2.5, adding an oxidant for oxidation, and performing ion exchange enrichment to obtain a vanadium-containing barren solution and a second solution, wherein the second solution is an eluent obtained by eluting with a sodium hydroxide solution; adding calcium oxide into the vanadium-containing barren solution, adjusting the pH value to 6.0-7.0, and returning to the multi-stage countercurrent leaching in the step (B) for recycling;
a step (E): adjusting the pH value of the second solution to 8.5-9.5, and adding the second solution in a mass ratio of 1: reacting 0.12 of 20% magnesium chloride solution at the temperature of 80-100 ℃ for 2 hours, and filtering to obtain a third solution;
step (F): adding vanadium to ammonium in a molar ratio of 1: 1.2, stirring and reacting at 40-60 ℃ for 2h, performing centrifugal separation to obtain ammonium metavanadate and a vanadium precipitation mother solution, removing ammonia from the vanadium precipitation mother solution through a degassing membrane, returning to the ore grinding step in the step (A) for use, finally performing decomposition reaction on the ammonium metavanadate to obtain vanadium pentoxide, performing decomposition reaction on the ammonium metavanadate to obtain vanadium pentoxide by adopting a calcination mode, wherein the calcination temperature is 500-550 ℃, the reaction time is 2-3 h, the ammonium metavanadate is decomposed to generate vanadium pentoxide, water and ammonia gas, absorbing the generated ammonia gas with sulfuric acid to obtain ammonium sulfate, dissolving the ammonium sulfate, and returning to the step (F) to react with the third solution.
Example 2
This example differs from example 1 in that: in the step (A), the water adding amount is controlled to obtain ore pulp with water content of 30%, concentrated sulfuric acid is added into the ore pulp in a reaction kettle, the ore pulp is uniformly stirred and cured at constant temperature for 5 hours, and the temperature is 120 ℃ to obtain a first reactant.
Example 3
This example differs from example 1 in that: in the step (A), the water adding amount is controlled to obtain ore pulp with the water content of 30%, the ore pulp with the water content of 30% is filtered by a ceramic filter to obtain wet ore powder with the water content of 20%, and the wet ore powder and concentrated sulfuric acid are aged for 5 hours at the temperature of 120 ℃ to obtain a first reactant.
Example 4
This example differs from example 1 in that: in the step (A), the water adding amount is controlled to obtain ore pulp with the water content of 30%, the ore pulp with the water content of 30% is filtered by a ceramic filter to obtain wet ore powder with the water content of 15%, and the wet ore powder and concentrated sulfuric acid are aged for 4 hours at the temperature of 120 ℃ to obtain a first reactant.
Example 5
This example differs from example 1 in that: in the step (A), the ore pulp is poured into a reaction kettle, and then concentrated sulfuric acid is directly poured into the reaction kettle, wherein the curing temperature is 110 ℃, and other conditions are the same.
Experimental example 1
The first reactant of the embodiments 1 to 4 of the present invention is detected, and the specific detection results are shown in the following table 1:
TABLE 1 ripening results for the first reactant
Comparative examples 1 to 10 in the table are comparative experiments according to examples 1 to 5, the comparative example 1 is compared with the comparative example 5, a pit is formed in ore pulp by stirring, and concentrated sulfuric acid is poured into the pit to improve a certain curing degree; generally speaking, when the water content of the ore pulp is 30-40%, the curing time is 5-6 h at the preferred temperature of 110-120 ℃, and when the water content of the ore pulp is 15-20%, the curing time is 4-5 h at the preferred temperature of 120-130 ℃.
Example 6
This example differs from example 1 in that: in the step (F), the ammonium metavanadate is decomposed to generate vanadium pentoxide, water and ammonia gas by adopting an electric heating mode; compared with calcination, the electric heating mode is more environment-friendly, waste such as calcination waste gas and waste residue can not be generated, and the factory environment is further optimized.
While particular embodiments of the present invention have been illustrated and described, it would be obvious that various other changes and modifications can be made without departing from the spirit and scope of the invention. It is therefore intended to cover in the appended claims all such changes and modifications that are within the scope of this invention.
Claims (10)
1. The method for preparing vanadium pentoxide is characterized by comprising the following steps:
(A) grinding stone coal by a wet grinding ball mill, simultaneously controlling the water addition amount to obtain ore pulp containing 30-40% of water, pouring the ore pulp into a reaction kettle, stirring along the middle to form a pit, pouring concentrated sulfuric acid into the pit, uniformly stirring, and curing at constant temperature for 4-6 h to obtain a first reactant;
(B) carrying out multi-stage countercurrent leaching separation on the first reactant at normal temperature to obtain a solid phase and a liquid phase, wherein the solid phase is ore tailings with the water content of less than 20% by mass, and the liquid phase is a vanadium-containing acid solution;
(C) adding a certain amount of ammonium bicarbonate or ammonium sulfate into the liquid phase, and performing solid-liquid separation to obtain ammonium alum crystals and a first solution;
(D) adjusting the pH value of the first solution to 2.0-2.5, adding an oxidant for oxidation, and performing ion exchange enrichment to obtain a vanadium-containing barren solution and a second solution, wherein the second solution is an eluent obtained by eluting with a sodium hydroxide solution;
(E) adjusting the pH value of the second solution to 8.5-9.5, and adding the second solution in a mass ratio of 1: reacting 0.12 of 20% magnesium chloride solution at the temperature of 80-100 ℃ for 2 hours, and filtering to obtain a third solution;
(F) adding vanadium to ammonium in a molar ratio of 1: 1.2, stirring and reacting for 2 hours at the temperature of 40-60 ℃, centrifugally separating to obtain ammonium metavanadate and vanadium precipitation mother liquor, and finally, carrying out decomposition reaction on the ammonium metavanadate to obtain vanadium pentoxide.
2. The method for producing vanadium pentoxide according to claim 1, wherein: in the step (A), the stone coal is ground to be less than 100 meshes by a wet grinding ball mill.
3. The method for producing vanadium pentoxide according to claim 1 or 2, wherein: and (B) curing the ore pulp and concentrated sulfuric acid in the step (A) for 5-6 h at the temperature of 110-120 ℃ to obtain a first reactant.
4. The method for producing vanadium pentoxide according to claim 1 or 2, wherein: and (B) enabling the ore pulp containing 30-40% of water in the step (A) to pass through a ceramic filter to obtain 15-20% of wet ore powder, and curing the wet ore powder and concentrated sulfuric acid at the temperature of 120-130 ℃ for 4-5 hours to obtain a first reactant.
5. The method for producing vanadium pentoxide according to claim 1 or 2, wherein: the molar ratio of ammonium ions in the ammonium bicarbonate or ammonium sulfate added in the step (C) to aluminum ions in the liquid phase is 1.2-1.5: 1.
6. the method for producing vanadium pentoxide according to claim 1 or 2, wherein: and (D) adding calcium oxide into the vanadium-containing barren solution enriched by the ion exchange column in the step (D), adjusting the pH value to 6.0-7.0, and returning to the step (B) for multi-stage countercurrent leaching for recycling.
7. The method for producing vanadium pentoxide according to claim 1 or 2, wherein: and (D) after deaminizing by a degassing membrane, returning the vanadium precipitation mother liquor obtained by centrifugal separation in the step (F) to the step (A) for ore grinding link application.
8. The method for producing vanadium pentoxide according to claim 1, wherein: in the step (F), the decomposition reaction of the ammonium metavanadate adopts a calcining mode, the calcining temperature is 500-550 ℃, the reaction time is 2-3 h, and the ammonium metavanadate is decomposed to generate vanadium pentoxide, water and ammonia gas.
9. The method for producing vanadium pentoxide according to claim 1, wherein: and (F) decomposing the ammonium metavanadate in the step (F) by adopting an electric heating mode to generate vanadium pentoxide, water and ammonia gas.
10. The method for producing vanadium pentoxide according to claim 8 or 9, wherein: and (D) absorbing ammonia gas generated by decomposing the ammonium metavanadate with sulfuric acid to obtain ammonium sulfate, dissolving the ammonium sulfate, and returning to the step (F) to react with the third solution.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910843176.6A CN110467222B (en) | 2019-09-06 | 2019-09-06 | Method for preparing vanadium pentoxide |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910843176.6A CN110467222B (en) | 2019-09-06 | 2019-09-06 | Method for preparing vanadium pentoxide |
Publications (2)
Publication Number | Publication Date |
---|---|
CN110467222A CN110467222A (en) | 2019-11-19 |
CN110467222B true CN110467222B (en) | 2021-11-23 |
Family
ID=68515111
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910843176.6A Active CN110467222B (en) | 2019-09-06 | 2019-09-06 | Method for preparing vanadium pentoxide |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110467222B (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWI856694B (en) * | 2023-06-09 | 2024-09-21 | 華鉬實業股份有限公司 | Preparation method of vanadium dioxide |
WO2025097457A1 (en) * | 2023-11-11 | 2025-05-15 | 洪江市钒盛钒业科技有限公司 | Method for preparing vanadium pentoxide |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101275187A (en) * | 2007-03-26 | 2008-10-01 | 吉首大学 | A stone coal wet vanadium extraction process |
CN101381103A (en) * | 2008-09-29 | 2009-03-11 | 浙江大学 | A method for extracting vanadium pentoxide by direct acid leaching of vanadium-containing stone coal ash slag |
CN101451199A (en) * | 2008-12-16 | 2009-06-10 | 中色(宁夏)东方集团有限公司 | Method for extracting vanadic anhydride from stone coal vanadium ore |
CN101723458A (en) * | 2009-12-01 | 2010-06-09 | 南阳西成科技有限公司 | Method for cleanly extracting vanadium pentexide from vanadium containing material |
CN101838749A (en) * | 2010-06-10 | 2010-09-22 | 中南大学 | Ion exchange extraction vanadium method of vanadium-containing solution |
CN104477992A (en) * | 2015-01-07 | 2015-04-01 | 攀钢集团研究院有限公司 | Method for preparing vanadium pentoxide |
-
2019
- 2019-09-06 CN CN201910843176.6A patent/CN110467222B/en active Active
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101275187A (en) * | 2007-03-26 | 2008-10-01 | 吉首大学 | A stone coal wet vanadium extraction process |
CN101381103A (en) * | 2008-09-29 | 2009-03-11 | 浙江大学 | A method for extracting vanadium pentoxide by direct acid leaching of vanadium-containing stone coal ash slag |
CN101451199A (en) * | 2008-12-16 | 2009-06-10 | 中色(宁夏)东方集团有限公司 | Method for extracting vanadic anhydride from stone coal vanadium ore |
CN101723458A (en) * | 2009-12-01 | 2010-06-09 | 南阳西成科技有限公司 | Method for cleanly extracting vanadium pentexide from vanadium containing material |
CN101838749A (en) * | 2010-06-10 | 2010-09-22 | 中南大学 | Ion exchange extraction vanadium method of vanadium-containing solution |
CN104477992A (en) * | 2015-01-07 | 2015-04-01 | 攀钢集团研究院有限公司 | Method for preparing vanadium pentoxide |
Also Published As
Publication number | Publication date |
---|---|
CN110467222A (en) | 2019-11-19 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2015161660A1 (en) | Method for preparing low-silicon vanadium pentoxide from solution containing vanadium, chromium and silicon | |
CN113279048B (en) | Method for preparing high-purity iron phosphate from iron-containing slag | |
CN111206150B (en) | Dissolved state high-similarity rare and precious metal enrichment and separation method based on floating extraction | |
CN101988154A (en) | New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps | |
CN110467222B (en) | Method for preparing vanadium pentoxide | |
EP2557067B1 (en) | Method for preparing manganese sulfate monohydrate | |
CN103436715A (en) | Method of extracting vanadium from stone coal | |
CN113651342A (en) | Method for producing lithium product by processing lepidolite through nitric acid atmospheric pressure method | |
CN103031443A (en) | Method of dealkalizing red mud and recovering aluminum and iron | |
CN115786732A (en) | Method for extracting lithium resource from clay type lithium ore | |
CN105200248B (en) | A kind of step of utilization carbide slag one neutralizes the method that titanium white waste acid prepares high-purity scandium | |
CN109022806A (en) | A method of utilizing the vanadium liquid removal of impurities clay standby vanadic anhydride of vanadium | |
CN109336177B (en) | Method for cleanly producing high-purity vanadium pentoxide by using hydrogen peroxide and ammonia water | |
CN105671324A (en) | Method for preparing ammonium rhenate from rhenium-enriched slags | |
CN110983054B (en) | Method for separating and recovering cobalt and nickel from manganese sulfate solution | |
CN106044730A (en) | Method for producing wet-process phosphoric acid from high-grade phosphate ore | |
CN105925812B (en) | A kind of method that manganese is extracted from Mn-rich slag | |
CN100357176C (en) | Method for recovering vitriol from waste vitrol containing metal salt | |
CN102925684A (en) | Method for preparing high-purity vanadium oxide | |
WO2025097457A1 (en) | Method for preparing vanadium pentoxide | |
CN108862382B (en) | Method for extracting high-purity vanadium pentoxide from lead vanadium ore | |
CN104386740B (en) | A kind of preparation method of high-purity fluorine calcium titanate | |
CN116022835B (en) | A resource treatment method for hazardous carbon-containing waste from aluminum electrolysis | |
CN104628033A (en) | Method for preparing metavanadate | |
CN115611311B (en) | Method for treating chromium-containing sludge generated by vanadium extraction wastewater |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |