CN114229877A - Method for decomposing phosphogypsum at low temperature - Google Patents
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- CN114229877A CN114229877A CN202210000610.6A CN202210000610A CN114229877A CN 114229877 A CN114229877 A CN 114229877A CN 202210000610 A CN202210000610 A CN 202210000610A CN 114229877 A CN114229877 A CN 114229877A
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- PASHVRUKOFIRIK-UHFFFAOYSA-L calcium sulfate dihydrate Chemical compound O.O.[Ca+2].[O-]S([O-])(=O)=O PASHVRUKOFIRIK-UHFFFAOYSA-L 0.000 title claims abstract description 115
- 238000000034 method Methods 0.000 title claims abstract description 35
- 238000000354 decomposition reaction Methods 0.000 claims abstract description 48
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 10
- 229910021645 metal ion Inorganic materials 0.000 claims abstract description 10
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 10
- 239000001301 oxygen Substances 0.000 claims abstract description 10
- 239000007789 gas Substances 0.000 claims description 23
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 18
- 238000001914 filtration Methods 0.000 claims description 15
- 230000008569 process Effects 0.000 claims description 11
- 239000000843 powder Substances 0.000 claims description 10
- 238000001354 calcination Methods 0.000 claims description 9
- 238000001035 drying Methods 0.000 claims description 9
- 229910052757 nitrogen Inorganic materials 0.000 claims description 9
- 238000002791 soaking Methods 0.000 claims description 6
- 238000005470 impregnation Methods 0.000 claims description 3
- 239000007788 liquid Substances 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 3
- 238000000227 grinding Methods 0.000 claims description 2
- 238000007873 sieving Methods 0.000 claims description 2
- 150000002500 ions Chemical class 0.000 claims 1
- 239000002184 metal Substances 0.000 claims 1
- 230000008901 benefit Effects 0.000 abstract description 3
- 239000000126 substance Substances 0.000 abstract description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 abstract description 2
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 2
- 239000011574 phosphorus Substances 0.000 abstract description 2
- 239000012299 nitrogen atmosphere Substances 0.000 abstract 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 20
- JGIATAMCQXIDNZ-UHFFFAOYSA-N calcium sulfide Chemical compound [Ca]=S JGIATAMCQXIDNZ-UHFFFAOYSA-N 0.000 description 16
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical group [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 15
- 238000006243 chemical reaction Methods 0.000 description 12
- 239000000292 calcium oxide Substances 0.000 description 11
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 10
- 230000002829 reductive effect Effects 0.000 description 9
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 8
- 238000006477 desulfuration reaction Methods 0.000 description 8
- 230000023556 desulfurization Effects 0.000 description 8
- 238000004364 calculation method Methods 0.000 description 7
- 239000003546 flue gas Substances 0.000 description 7
- 230000003647 oxidation Effects 0.000 description 7
- 238000007254 oxidation reaction Methods 0.000 description 7
- 239000000047 product Substances 0.000 description 7
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 6
- 239000011541 reaction mixture Substances 0.000 description 6
- 239000007787 solid Substances 0.000 description 6
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 5
- 229910021586 Nickel(II) chloride Inorganic materials 0.000 description 5
- 239000004568 cement Substances 0.000 description 5
- GVPFVAHMJGGAJG-UHFFFAOYSA-L cobalt dichloride Chemical compound [Cl-].[Cl-].[Co+2] GVPFVAHMJGGAJG-UHFFFAOYSA-L 0.000 description 5
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 5
- QMMRZOWCJAIUJA-UHFFFAOYSA-L nickel dichloride Chemical compound Cl[Ni]Cl QMMRZOWCJAIUJA-UHFFFAOYSA-L 0.000 description 5
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- 239000002253 acid Substances 0.000 description 4
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 4
- 239000003638 chemical reducing agent Substances 0.000 description 4
- 238000005265 energy consumption Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000002994 raw material Substances 0.000 description 4
- 229910002091 carbon monoxide Inorganic materials 0.000 description 3
- 239000003054 catalyst Substances 0.000 description 3
- 239000002131 composite material Substances 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- 229910019142 PO4 Inorganic materials 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 229910052681 coesite Inorganic materials 0.000 description 2
- 229910052593 corundum Inorganic materials 0.000 description 2
- 229910052906 cristobalite Inorganic materials 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 2
- 239000010452 phosphate Substances 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 239000002910 solid waste Substances 0.000 description 2
- 229910052682 stishovite Inorganic materials 0.000 description 2
- 229910052905 tridymite Inorganic materials 0.000 description 2
- 229910001845 yogo sapphire Inorganic materials 0.000 description 2
- 239000005997 Calcium carbide Substances 0.000 description 1
- ZKQDCIXGCQPQNV-UHFFFAOYSA-N Calcium hypochlorite Chemical compound [Ca+2].Cl[O-].Cl[O-] ZKQDCIXGCQPQNV-UHFFFAOYSA-N 0.000 description 1
- 229910001030 Iron–nickel alloy Inorganic materials 0.000 description 1
- KKCBUQHMOMHUOY-UHFFFAOYSA-N Na2O Inorganic materials [O-2].[Na+].[Na+] KKCBUQHMOMHUOY-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 238000012271 agricultural production Methods 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- 239000007844 bleaching agent Substances 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 229940043430 calcium compound Drugs 0.000 description 1
- 150000001674 calcium compounds Chemical class 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 239000002274 desiccant Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000007598 dipping method Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- PXHVJJICTQNCMI-UHFFFAOYSA-N nickel Substances [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 235000017550 sodium carbonate Nutrition 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- CLZWAWBPWVRRGI-UHFFFAOYSA-N tert-butyl 2-[2-[2-[2-[bis[2-[(2-methylpropan-2-yl)oxy]-2-oxoethyl]amino]-5-bromophenoxy]ethoxy]-4-methyl-n-[2-[(2-methylpropan-2-yl)oxy]-2-oxoethyl]anilino]acetate Chemical compound CC1=CC=C(N(CC(=O)OC(C)(C)C)CC(=O)OC(C)(C)C)C(OCCOC=2C(=CC=C(Br)C=2)N(CC(=O)OC(C)(C)C)CC(=O)OC(C)(C)C)=C1 CLZWAWBPWVRRGI-UHFFFAOYSA-N 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/02—Oxides or hydroxides
- C01F11/04—Oxides or hydroxides by thermal decomposition
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2/00—Lime, magnesia or dolomite
- C04B2/005—Lime, magnesia or dolomite obtained from an industrial by-product
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Ceramic Engineering (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Thermal Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Physics & Mathematics (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Catalysts (AREA)
Abstract
The invention provides a method for decomposing phosphogypsum at low temperature, and belongs to the technical field of phosphorus chemical treatment. The specific scheme is as follows: pretreating phosphogypsum in a metal ion solution, putting the dried phosphogypsum into a tube furnace, introducing CO in a nitrogen atmosphere, and introducing the CO at 500-900 DEG CoAnd C, reducing the phosphogypsum into CaS, and then switching oxygen to oxidize the CaS into CaO so as to realize low-temperature decomposition of the phosphogypsum. The method has the advantages of low decomposition temperature, wide application prospect and the like.
Description
Technical Field
The invention relates to a method for decomposing phosphogypsum at low temperature, in particular to the method for decomposing the phosphogypsum by two steps, which has simple process and lower decomposition temperature and belongs to the technical field of phosphorus chemical treatment.
Background
Phosphogypsum is a solid waste generated by the reaction of sulfuric acid and phosphate ore in the production process of industrial wet-process phosphoric acid, and the main component of the phosphogypsum is calcium sulfate dihydrate (CaSO)4·2H2O), the impurities are mainly SiO2、P2O5F compounds, and metal oxides such as Mg and Al. China is used as the first country for producing large phosphate fertilizers and the first country for producing phosphogypsum as a byproduct in the world, and about 4-5 tons of phosphogypsum are produced in each 1 ton of phosphoric acid prepared in the wet-process phosphoric acid production process. While the phosphorization industry is rapidly developed, the phosphogypsum also becomes a problem which is difficult to solve in the industry. The accumulated amount of phosphogypsum in China exceeds 7 hundred million tons, the annual emission amount is up to 8000 ten thousand tons, and the utilization rate is less than 40 percent. Most phosphogypsum is directly piled in the open air or poured into the sea, which not only causes resource waste and environmental pollution, but also influences social development and threatens human safety. The phosphogypsum is widely applied to the aspects of building materials, chemical products, agricultural production and the like at present, wherein the most consumed phosphogypsum is decomposed to prepare CaO and coproduce sulfuric acid. The technical problems of high decomposition energy consumption, high decomposition temperature, large investment economic cost, unsatisfactory later-period economic benefit and the like of the phosphogypsum need to be improved. Therefore, lowering the decomposition temperature of phosphogypsum and increasing the benefit are the most important research directions at present.
The invention patent CN101357773B discloses a method for reducing the decomposition temperature of phosphogypsum, which comprises respectively using gaseous reducing agents CO and H2S, adding powder of solid reducing agents such as fly ash, coal gangue and the like and gas-solid, solid-solid composite reducing agents serving as additives into phosphogypsum for decomposition, adopting double-atmosphere reaction to reduce the decomposition temperature of the phosphogypsum and ensure high decomposition rate and desulfurization rate, and reducing the decomposition temperature of the phosphogypsum to be less than or equal to 1000oC, decomposition rate is more than or equal to 95 percent, and SO can be stably recovered2And (4) resources.
The invention patent CN101186281B discloses a method for reducing the decomposition temperature of phosphogypsum in the process of producing acid by phosphogypsum, coal is used as a reducing agent in the process of producing acid by phosphogypsum and co-producing cement clinker, and MgO, NaCl and SiO are added2、Al2O3、Fe2O3A composite catalyst as main component, which is prepared from ardealiteThe decomposition temperature is reduced to 700-750 deg.CoC, energy consumption is reduced, and the generated calcium compound can be directly used as high-quality cement clinker and SO2Can be directly used as acid-making raw materials.
The invention patent CN105036170A discloses a method for preparing calcium oxide by decomposing phosphogypsum, which decomposes and generates CaO in a reducing atmosphere-oxidizing atmosphere for two times in a circulating way, and the generated CaO can be used as a filling agent and a drying agent to prepare calcium carbide, soda ash, bleaching powder and the like.
The invention patent CN101456542A discloses a method for reductive decomposition of phosphogypsum by carbon monoxide at a temperature of 750-850 DEG CoC,N2Introducing CO to reduce and decompose the phosphogypsum under the atmosphere. SO in tail gas2The volume percentage content is more than or equal to 10 percent, the solid slag material can be directly used as qualified raw material gas for producing sulfuric acid by the two-conversion and two-absorption acid making process, the solid slag material component is more than or equal to 70 weight percent of CaO, and the solid slag material can be used as cement clinker.
The invention patent CN103466675A discloses a method for decomposing phosphogypsum at low temperature, which uses Fe-Ni composite catalysis to decompose phosphogypsum under the atmosphere of carbon monoxide, and reduces the decomposition temperature of the phosphogypsum to 570-630%oC, the aim of saving energy and reducing consumption is achieved, the generated CaO can be used as high-quality cement clinker, and the generated SO2Can be used as raw material gas for preparing acid.
The prior phosphogypsum decomposition technology generally has the following problems: higher decomposition temperature, complex decomposition process, more product components, lower product yield and high energy consumption. If the method can simplify the operation steps, increase the product yield and simplify the product components on the basis of reducing the decomposition temperature of the phosphogypsum, create conditions for the resource utilization of the phosphogypsum and increase the recovery utilization rate of resources.
Disclosure of Invention
The invention provides a simple and effective method for decomposing phosphogypsum at low temperature. The method takes carbon monoxide as a reducing gas and ferric chloride, cobalt chloride and nickel chloride as catalytic auxiliaries, and reduces the decomposition temperature of phosphogypsum to 500-900 DEG CoAnd C, simplifying operation steps, improving the decomposition rate and improving the product purity.
The patent aims to provide a method for decomposing phosphogypsum at low temperature, which is characterized by comprising the following steps:
(1) crushing, grinding and sieving the phosphogypsum.
(2) Soaking the screened 100-120-mesh phosphogypsum powder in a metal ion impregnation liquid, and stirring for 8-12 h, wherein the metal ion impregnation liquid contains Fe3+、Co2+、Ni2+At least one of (1) in the impregnating solution, Fe3+The concentration of (A) is 0.4 to 0.8 mol/L, Co2+The concentration of (A) is 0.4 to 0.6 mol/L, Ni2+The concentration of the filter residue is 0.4-0.6 mol/L, and the filtered filter residue is 110-130 mol/LoAnd C, drying for 1-2 h to obtain the pretreated phosphogypsum.
(3) And (3) putting the phosphogypsum obtained in the step (2) into a tube furnace, and introducing nitrogen for 3-5 min. Switching the gas to CO with the purity of 99.99 percent and decomposing at the temperature of 500-900 DEG CoCalcining for 30-120 min under C, and reducing the phosphogypsum into CaS.
(4) And (4) after the step (3) is finished, switching the gas in the tubular furnace into oxygen at the decomposition temperature, and introducing for 30-90 min to oxidize the CaS into CaO.
The phosphogypsum has complex components, more byproducts, complex decomposition mechanism, high heat absorption and high decomposition temperature in the decomposition process. Under the reducing atmosphere, the addition of metal ions can reduce the decomposition temperature of the phosphogypsum and promote the decomposition of the phosphogypsum; the method decomposes the phosphogypsum into calcium sulfide and then converts the calcium sulfide into calcium oxide, so that the decomposition temperature of the phosphogypsum can be reduced, the energy required by decomposition is reduced, and the operation is simple and easy. Under the atmosphere of quantitative CO reduction, metal ion catalysis is adopted, and the solution containing metal ions used in the experiment is Fe3+、Co2+、Ni2+At least one of the above-mentioned materials is used for decomposing phosphogypsum by steps by switching gas required by reaction, and the main products obtained by experiment are CaO and SO2。
In a CO reduction atmosphere, decomposing phosphogypsum by adopting metal ions after dipping and then oxidizing, wherein the main reaction in the process is as follows:
the phosphogypsum is solid waste generated by a wet-process phosphoric acid process, and the main components of the phosphogypsum are shown in a table 1:
table 1: main component of phosphogypsum raw material
Composition (I) | Content (%) | Composition (I) | Content (%) |
SO3 | 49.77 | Fe2O3 | 0.13 |
CaO | 41.29 | BaO | 0.1 |
SiO2 | 5.99 | SrO | 0.09 |
P2O5 | 0.94 | Na2O | 0.07 |
F | 0.86 | K2O | 0.06 |
Al2O3 | 0.67 | MgO | 0.02 |
The device for decomposing phosphogypsum at low temperature is shown in the attached drawing.
The invention has the beneficial effects that:
(1) the method has simple process and low energy consumption, and reduces the decomposition temperature of the phosphogypsum to 500-900 DEG CoC。
(2) The present patent proposes a new metal ion catalyst system.
(3)Fe3+、Co2+、Ni2+Are all common metal ions, and the amount of the catalyst used is small,
(4) the method provided by the invention is beneficial to reducing the temperature in the process of preparing CaO and co-producing cement by decomposing phosphogypsum, and has wide application prospect.
Drawings
FIG. 1 is a diagram of an experimental apparatus of the present invention.
Detailed Description
The present invention will be described in further detail with reference to examples, but the scope of the present invention is not limited to the examples.
In the description of the embodiments of the present invention, it is to be understood that "-" and "-" denote ranges of two numerical values, and the ranges include endpoints. For example: "A-B" means a range of greater than or equal to A and less than or equal to B. "A to B" means a range of not less than A and not more than B.
In the description of the embodiments of the present invention, the term "and/or" herein is only one kind of association relationship describing an associated object, and means that there may be three kinds of relationships, for example, a and/or B, and may mean: a exists alone, A and B exist simultaneously, and B exists alone. In addition, the character "/" herein generally indicates that the former and latter related objects are in an "or" relationship.
Although embodiments of the present invention have been shown and described, it will be appreciated by those skilled in the art that changes, modifications, substitutions and alterations can be made in these embodiments without departing from the principles and spirit of the invention, the scope of which is defined in the appended claims and their equivalents.
Example 1:
the phosphogypsum is crushed, ground and sieved by a 100-mesh sieve. Soaking the screened phosphogypsum powder in ferric chloride solution (Fe)3+0.8 mol/L) for 12 hours, and filtering residue after filtration is at 110oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and introducing the CO into the tube furnace at 900 DEGoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4The molar ratio is 3.5:1, and the phosphogypsum is reduced into CaS. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 30 min for oxidation. After the reaction, the reaction mixture was cooled to room temperature and the S content in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the determination and calculation result shows that the decomposition rate of the phosphogypsum in the embodiment is 95.9 percent, and the content of calcium sulfide in the residue is 29.2 percent.
Example 2:
the phosphogypsum is crushed, ground and sieved by a 100-mesh sieve. Soaking the screened phosphogypsum powder in cobalt chloride solution (Co)2+0.6 mol/L) for 12 hours, and filtering residue after filtration is at 110oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Placing the pretreated phosphogypsum into a tube furnaceIntroducing CO with the purity of 99.99 percent under the protection of nitrogen, and introducing the CO at 900 DEG CoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4The molar ratio is 3.5:1, and the phosphogypsum is reduced into CaS. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 30 min for oxidation. After the reaction, the reaction mixture was cooled to room temperature and the S content in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the determination and calculation result shows that the decomposition rate of the phosphogypsum in the embodiment is 95.4 percent, and the content of calcium sulfide in the residue is 29.3 percent.
Example 3:
the phosphogypsum is crushed, ground and sieved by a 100-mesh sieve. Soaking the screened phosphogypsum powder in nickel chloride solution (Ni)2+0.6 mol/L) for 12 hours, and filtering residue after filtration is at 110oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and introducing the CO into the tube furnace at 900 DEGoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4The molar ratio is 3.5:1, and the phosphogypsum is reduced into CaS. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 30 min for oxidation. After the reaction, the reaction mixture was cooled to room temperature and the S content in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the determination and calculation result shows that the decomposition rate of the phosphogypsum in the embodiment is 96.3 percent, and the content of calcium sulfide in the residue is 29.2 percent.
Example 4:
the phosphogypsum is crushed, ground and sieved by a sieve with 110 meshes. Immersing the screened phosphogypsum powder in a solution (Fe) containing ferric chloride and cobalt chloride3+Has a concentration of 0.6 mol/L, Co2+0.5 mol/L) for 11 hours, and filtering residue after filtration is 120oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and reacting at 800 DEG CoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4Reducing the phosphogypsum into CaS with the molar ratio of 4: 1. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 60 min for oxidation. After the reaction, the reaction mixture was naturally cooled to room temperature, and S in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the determination and calculation result shows that the decomposition of the phosphogypsum in the embodiment is 96.1 percent, and the content of calcium sulfide in the residue is 28.9 percent.
Example 5:
the phosphogypsum is crushed, ground and sieved by a sieve with 110 meshes. Immersing the screened phosphogypsum powder in a solution (Fe) containing ferric chloride and nickel chloride3+Has a concentration of 0.6 mol/L, Ni2+0.5 mol/L) for 11 hours, and filtering residue after filtration is 120oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and reacting at 800 DEG CoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4Reducing the phosphogypsum into CaS with the molar ratio of 4: 1. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 60 min for oxidation. After the reaction is finished, naturally cooling to room temperature,iodometric determination of S in the residue2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the decomposition of the phosphogypsum in the embodiment is 95.4 percent and the content of calcium sulfide in the residue is 29 percent through measurement and calculation.
Example 6:
the phosphogypsum is crushed, ground and sieved by a sieve with 110 meshes. Immersing the screened phosphogypsum powder in a solution (Co) containing cobalt chloride and nickel chloride2+Has a concentration of 0.5 mol/L, Ni2+0.5 mol/L) for 11 hours, and filtering residue after filtration is 120oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and reacting at 800 DEG CoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4Reducing the phosphogypsum into CaS with the molar ratio of 4: 1. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 60 min for oxidation. After the reaction, the reaction mixture was naturally cooled to room temperature, and S in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the decomposition of phosphogypsum in the example is 95.7% and the content of calcium sulfide in the residue is 28.5% through measurement and calculation.
Example 7:
the phosphogypsum is crushed, ground and sieved by a 120-mesh sieve. Immersing the screened phosphogypsum powder in a solution (Fe) containing ferric chloride, nickel chloride and cobalt chloride3+Has a concentration of 0.4 mol/L、Co2+Has a concentration of 0.4 mol/L, Ni2+0.4 mol/L) for 10 hours, and filtering residue after filtration is put in a stirring tank of 130oAnd C, drying for 2 h to obtain the pretreated phosphogypsum. Putting the pretreated phosphogypsum into a tube furnace, introducing CO with the purity of 99.99 percent under the protection of nitrogen, and introducing the CO into the tube furnace at 700 DEGoCalcining for 1 h at the temperature of C, introducing CO gas and CaSO in phosphogypsum4The molar ratio is 4.5:1, and the phosphogypsum is reduced into CaS. And after the steps are finished, switching the gas in the tubular furnace to oxygen, and introducing for 90 min for oxidation. After the reaction, the reaction mixture was naturally cooled to room temperature, and S in the residue was measured by iodometry2-And (4) calculating the desulfurization rate by using a flue gas analyzer, and then calculating the amount of calcium sulfate and calcium sulfide in the residue. The decomposition rate of phosphogypsum can be calculated according to the following formula:
the decomposition of phosphogypsum in the example is 97.1% and the content of calcium sulfide in the residue is 27.3% through measurement and calculation.
Claims (4)
1. A method for decomposing phosphogypsum at low temperature mainly comprises the following steps:
(1) crushing, grinding and sieving the phosphogypsum.
(2) Soaking phosphogypsum powder in a soaking solution containing metal ions, stirring for 8-12 h, and filtering to obtain filter residues at 110-130%oAnd C, drying to obtain the pretreated phosphogypsum.
(3) And (3) putting the phosphogypsum obtained in the step (2) into a tube furnace, and introducing nitrogen for 3-5 min. And switching gas to CO, calcining for 30-90 min at a certain decomposition temperature, and reducing phosphogypsum to CaS.
(4) And (4) after the step (3) is finished, switching to oxygen in the tubular furnace, and introducing for 30-120 min to oxidize the CaS into CaO.
2. The process of low temperature decomposition of phosphogypsum according to claim 1, characterized in that in step (2) the metal is containedThe ion impregnation liquid contains Fe3+、Co2+、Ni2+At least one of (1).
3. The method for decomposing phosphogypsum at low temperature according to claim 1, wherein the decomposition temperature of the phosphogypsum in the step (3) is 500-900 ~oC。
4. The method of claim 1, wherein the CO gas is introduced with the CaSO in phosphogypsum4The molar ratio is 3.5-4.5: 1.
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Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101456542A (en) * | 2009-01-09 | 2009-06-17 | 昆明理工大学 | Method for reducing and decomposing phosphogypsum by carbon monoxide |
CN103408052A (en) * | 2013-07-25 | 2013-11-27 | 昆明理工大学 | Decomposition method of ardealite |
CN103466675A (en) * | 2013-09-03 | 2013-12-25 | 昆明理工大学 | Decomposition method of ardealite |
CN105036170A (en) * | 2015-07-27 | 2015-11-11 | 昆明理工大学 | Method for preparing calcium oxide through phosphogypsum decomposition |
WO2019103586A1 (en) * | 2017-11-22 | 2019-05-31 | Ocp Sa | Phosphogypsum decomposition process |
CN113603126A (en) * | 2021-09-17 | 2021-11-05 | 中国科学院过程工程研究所 | Method for preparing calcium oxide by using industrial byproduct gypsum |
-
2022
- 2022-01-04 CN CN202210000610.6A patent/CN114229877A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101456542A (en) * | 2009-01-09 | 2009-06-17 | 昆明理工大学 | Method for reducing and decomposing phosphogypsum by carbon monoxide |
CN103408052A (en) * | 2013-07-25 | 2013-11-27 | 昆明理工大学 | Decomposition method of ardealite |
CN103466675A (en) * | 2013-09-03 | 2013-12-25 | 昆明理工大学 | Decomposition method of ardealite |
CN105036170A (en) * | 2015-07-27 | 2015-11-11 | 昆明理工大学 | Method for preparing calcium oxide through phosphogypsum decomposition |
WO2019103586A1 (en) * | 2017-11-22 | 2019-05-31 | Ocp Sa | Phosphogypsum decomposition process |
CN113603126A (en) * | 2021-09-17 | 2021-11-05 | 中国科学院过程工程研究所 | Method for preparing calcium oxide by using industrial byproduct gypsum |
Non-Patent Citations (2)
Title |
---|
肖国先, 周松林, 胡道和: "磷石膏在还原──氧化双气氛下的分解反应动力学研究", 水泥, no. 08, 10 August 1997 (1997-08-10), pages 1 - 3 * |
郑大龙等: ""不同气氛条件下磷石膏分解过程变迁模拟研究"", 《计算机与应用化学》, 28 November 2016 (2016-11-28), pages 1177 - 1181 * |
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