CN106977123A - A kind of citric acid for being used to remove impurity fluorine in ardealite adds water the process washed - Google Patents
A kind of citric acid for being used to remove impurity fluorine in ardealite adds water the process washed Download PDFInfo
- Publication number
- CN106977123A CN106977123A CN201710204685.5A CN201710204685A CN106977123A CN 106977123 A CN106977123 A CN 106977123A CN 201710204685 A CN201710204685 A CN 201710204685A CN 106977123 A CN106977123 A CN 106977123A
- Authority
- CN
- China
- Prior art keywords
- phosphogypsum
- citric acid
- washing
- water
- fluorine
- Prior art date
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- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 title claims abstract description 288
- 238000000034 method Methods 0.000 title claims abstract description 106
- 239000012535 impurity Substances 0.000 title claims abstract description 72
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 67
- 239000011737 fluorine Substances 0.000 title claims abstract description 53
- 229910052731 fluorine Inorganic materials 0.000 title claims abstract description 53
- 230000008569 process Effects 0.000 title claims abstract description 40
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 title abstract 3
- PASHVRUKOFIRIK-UHFFFAOYSA-L calcium sulfate dihydrate Chemical compound O.O.[Ca+2].[O-]S([O-])(=O)=O PASHVRUKOFIRIK-UHFFFAOYSA-L 0.000 claims abstract description 227
- 238000005406 washing Methods 0.000 claims abstract description 73
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 52
- 238000004519 manufacturing process Methods 0.000 claims abstract description 44
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 claims abstract description 29
- 239000007864 aqueous solution Substances 0.000 claims abstract description 28
- 239000004568 cement Substances 0.000 claims abstract description 27
- 239000000243 solution Substances 0.000 claims abstract description 24
- 239000002253 acid Substances 0.000 claims abstract description 19
- 239000000126 substance Substances 0.000 claims abstract description 17
- 238000001035 drying Methods 0.000 claims abstract description 15
- 238000002360 preparation method Methods 0.000 claims abstract description 15
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 14
- 239000003546 flue gas Substances 0.000 claims abstract description 14
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims abstract description 11
- 235000011941 Tilia x europaea Nutrition 0.000 claims abstract description 11
- 239000004571 lime Substances 0.000 claims abstract description 11
- 239000002351 wastewater Substances 0.000 claims abstract description 11
- 229910019142 PO4 Inorganic materials 0.000 claims abstract description 9
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims abstract description 8
- 239000010452 phosphate Substances 0.000 claims abstract description 8
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims description 48
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 22
- 239000002994 raw material Substances 0.000 claims description 18
- 239000002002 slurry Substances 0.000 claims description 17
- 239000000047 product Substances 0.000 claims description 13
- 239000002699 waste material Substances 0.000 claims description 13
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 11
- 239000000203 mixture Substances 0.000 claims description 11
- 238000003756 stirring Methods 0.000 claims description 11
- 239000007788 liquid Substances 0.000 claims description 9
- 239000013049 sediment Substances 0.000 claims description 9
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 8
- 239000000523 sample Substances 0.000 claims description 8
- 239000002910 solid waste Substances 0.000 claims description 8
- 229940037003 alum Drugs 0.000 claims description 6
- 238000006386 neutralization reaction Methods 0.000 claims description 6
- 238000005119 centrifugation Methods 0.000 claims description 5
- 239000000706 filtrate Substances 0.000 claims description 5
- 239000008367 deionised water Substances 0.000 claims description 4
- 229910021641 deionized water Inorganic materials 0.000 claims description 4
- 238000004090 dissolution Methods 0.000 claims description 4
- 238000005485 electric heating Methods 0.000 claims description 4
- 238000013517 stratification Methods 0.000 claims description 4
- 238000004065 wastewater treatment Methods 0.000 claims description 4
- 230000009471 action Effects 0.000 claims description 3
- 238000005554 pickling Methods 0.000 claims description 3
- 229910004261 CaF 2 Inorganic materials 0.000 claims description 2
- 125000001153 fluoro group Chemical group F* 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims 1
- 238000000746 purification Methods 0.000 abstract description 9
- 230000007797 corrosion Effects 0.000 abstract description 2
- 238000005260 corrosion Methods 0.000 abstract description 2
- 239000010440 gypsum Substances 0.000 description 14
- 229910052602 gypsum Inorganic materials 0.000 description 14
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 12
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 11
- 239000011575 calcium Substances 0.000 description 11
- 239000005416 organic matter Substances 0.000 description 11
- 239000011574 phosphorus Substances 0.000 description 11
- 229910052698 phosphorus Inorganic materials 0.000 description 11
- 238000011160 research Methods 0.000 description 11
- 238000006115 defluorination reaction Methods 0.000 description 8
- 238000002386 leaching Methods 0.000 description 8
- 229910052761 rare earth metal Inorganic materials 0.000 description 8
- 238000001179 sorption measurement Methods 0.000 description 8
- 230000008901 benefit Effects 0.000 description 7
- 230000000694 effects Effects 0.000 description 7
- 239000010410 layer Substances 0.000 description 7
- 235000021317 phosphate Nutrition 0.000 description 7
- 239000002244 precipitate Substances 0.000 description 7
- 239000011593 sulfur Substances 0.000 description 7
- 229910052717 sulfur Inorganic materials 0.000 description 7
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 6
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 6
- 238000011161 development Methods 0.000 description 6
- 230000007613 environmental effect Effects 0.000 description 6
- 229910052588 hydroxylapatite Inorganic materials 0.000 description 6
- XYJRXVWERLGGKC-UHFFFAOYSA-D pentacalcium;hydroxide;triphosphate Chemical compound [OH-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O XYJRXVWERLGGKC-UHFFFAOYSA-D 0.000 description 6
- 230000002378 acidificating effect Effects 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 5
- 239000003795 chemical substances by application Substances 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- 150000002910 rare earth metals Chemical class 0.000 description 5
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 4
- XUIMIQQOPSSXEZ-UHFFFAOYSA-N Silicon Chemical compound [Si] XUIMIQQOPSSXEZ-UHFFFAOYSA-N 0.000 description 4
- -1 alkali metal salts Chemical class 0.000 description 4
- 229910052791 calcium Inorganic materials 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- 238000003912 environmental pollution Methods 0.000 description 4
- 238000001914 filtration Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 238000000926 separation method Methods 0.000 description 4
- 229910052710 silicon Inorganic materials 0.000 description 4
- 239000010703 silicon Substances 0.000 description 4
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 3
- 229910004298 SiO 2 Inorganic materials 0.000 description 3
- 238000002441 X-ray diffraction Methods 0.000 description 3
- 238000009825 accumulation Methods 0.000 description 3
- 239000003463 adsorbent Substances 0.000 description 3
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 3
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 3
- 235000011130 ammonium sulphate Nutrition 0.000 description 3
- 239000003638 chemical reducing agent Substances 0.000 description 3
- 230000006378 damage Effects 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 239000003337 fertilizer Substances 0.000 description 3
- 238000005188 flotation Methods 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000011229 interlayer Substances 0.000 description 3
- 239000010453 quartz Substances 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 238000001878 scanning electron micrograph Methods 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- 229910002651 NO3 Inorganic materials 0.000 description 2
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 2
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 239000000654 additive Substances 0.000 description 2
- 229910021529 ammonia Inorganic materials 0.000 description 2
- 229910052586 apatite Inorganic materials 0.000 description 2
- 239000004566 building material Substances 0.000 description 2
- 239000006227 byproduct Substances 0.000 description 2
- 238000001354 calcination Methods 0.000 description 2
- 229910000019 calcium carbonate Inorganic materials 0.000 description 2
- 229910001424 calcium ion Inorganic materials 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000010790 dilution Methods 0.000 description 2
- 239000012895 dilution Substances 0.000 description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 2
- 230000003628 erosive effect Effects 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 230000005484 gravity Effects 0.000 description 2
- 239000011507 gypsum plaster Substances 0.000 description 2
- 230000036571 hydration Effects 0.000 description 2
- 238000006703 hydration reaction Methods 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 229910017604 nitric acid Inorganic materials 0.000 description 2
- VSIIXMUUUJUKCM-UHFFFAOYSA-D pentacalcium;fluoride;triphosphate Chemical compound [F-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O VSIIXMUUUJUKCM-UHFFFAOYSA-D 0.000 description 2
- 239000002686 phosphate fertilizer Substances 0.000 description 2
- 229940088417 precipitated calcium carbonate Drugs 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 239000012521 purified sample Substances 0.000 description 2
- 230000002285 radioactive effect Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 238000001228 spectrum Methods 0.000 description 2
- 230000001755 vocal effect Effects 0.000 description 2
- 239000010457 zeolite Substances 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical group [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 229910052770 Uranium Inorganic materials 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- PTFCDOFLOPIGGS-UHFFFAOYSA-N Zinc dication Chemical compound [Zn+2] PTFCDOFLOPIGGS-UHFFFAOYSA-N 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 229910052925 anhydrite Inorganic materials 0.000 description 1
- 239000003146 anticoagulant agent Substances 0.000 description 1
- 229940127219 anticoagulant drug Drugs 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000008280 blood Substances 0.000 description 1
- 210000004369 blood Anatomy 0.000 description 1
- 230000023555 blood coagulation Effects 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000003889 chemical engineering Methods 0.000 description 1
- 239000013064 chemical raw material Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 239000008139 complexing agent Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 230000007123 defense Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000004455 differential thermal analysis Methods 0.000 description 1
- 150000004683 dihydrates Chemical class 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 239000003721 gunpowder Substances 0.000 description 1
- 230000008676 import Effects 0.000 description 1
- 238000000338 in vitro Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 238000001000 micrograph Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 239000012299 nitrogen atmosphere Substances 0.000 description 1
- 239000002367 phosphate rock Substances 0.000 description 1
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 1
- 235000021110 pickles Nutrition 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000003755 preservative agent Substances 0.000 description 1
- 230000002335 preservative effect Effects 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 238000011112 process operation Methods 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- NIFIFKQPDTWWGU-UHFFFAOYSA-N pyrite Chemical compound [Fe+2].[S-][S-] NIFIFKQPDTWWGU-UHFFFAOYSA-N 0.000 description 1
- 229910052683 pyrite Inorganic materials 0.000 description 1
- 239000011028 pyrite Substances 0.000 description 1
- 229910052705 radium Inorganic materials 0.000 description 1
- HCWPIIXVSYCSAN-UHFFFAOYSA-N radium atom Chemical compound [Ra] HCWPIIXVSYCSAN-UHFFFAOYSA-N 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000004626 scanning electron microscopy Methods 0.000 description 1
- 239000003566 sealing material Substances 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000002364 soil amendment Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000009270 solid waste treatment Methods 0.000 description 1
- 239000002594 sorbent Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000002411 thermogravimetry Methods 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
- 238000001132 ultrasonic dispersion Methods 0.000 description 1
- DNYWZCXLKNTFFI-UHFFFAOYSA-N uranium Chemical compound [U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U][U] DNYWZCXLKNTFFI-UHFFFAOYSA-N 0.000 description 1
- 238000004876 x-ray fluorescence Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
-
- 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
- C04B11/00—Calcium sulfate cements
- C04B11/26—Calcium sulfate cements strating from chemical gypsum; starting from phosphogypsum or from waste, e.g. purification products of smoke
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B17/00—Sulfur; Compounds thereof
- C01B17/69—Sulfur trioxide; Sulfuric acid
- C01B17/74—Preparation
- C01B17/745—Preparation from sulfates
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Ceramic Engineering (AREA)
- Materials Engineering (AREA)
- Structural Engineering (AREA)
- Inorganic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
一种用于去除磷石膏中杂质氟的柠檬酸加水洗的工艺方法,包括柠檬酸溶解、柠檬酸洗涤和水洗三道工序,所述的柠檬酸加水洗的工艺方法的制备过程包括如下三个步骤:首先,配制不同浓度柠檬酸水溶液备用,其次,用上述配制好的柠檬酸溶液加水洗处理磷石膏,最后,利用石灰中和处理水洗废水,溶液中柠檬酸可与磷石膏中杂质发生化学作用,使磷石膏中氟化物和磷酸盐等杂质转化成可水洗的易溶性物质,再通过水洗工艺进行除杂,使净化后,降低设备中和烘干烟气中氟化物含量,去除了氟化物和磷化物的磷石膏能够被磷石膏制酸联产水泥工艺利用,由于氟化物去除,不会再对硫酸和水泥生产工艺工段设备造成腐蚀。A process for removing impurity fluorine in phosphogypsum by washing with citric acid and water, comprising three steps of dissolving citric acid, washing with citric acid and washing with water, the preparation process of the process of washing with citric acid includes the following three steps: Steps: firstly, prepare different concentrations of citric acid aqueous solutions for later use; secondly, use the above-prepared citric acid solution to add water to wash the phosphogypsum; finally, use lime to neutralize the washing wastewater. function, transform impurities such as fluoride and phosphate in phosphogypsum into washable soluble substances, and then remove impurities through water washing process, so that after purification, reduce the fluoride content in the equipment and in the drying flue gas, and remove the fluorine The phosphogypsum of fluoride and phosphide can be used by the phosphogypsum acid co-production cement process. Due to the removal of fluoride, it will no longer cause corrosion to the equipment in the sulfuric acid and cement production process.
Description
技术领域technical field
本发明涉及的是去除磷石膏中杂质氟的方法,属于工业固体废弃物处理与处置技术领域。The invention relates to a method for removing impurity fluorine in phosphogypsum, and belongs to the technical field of industrial solid waste treatment and disposal.
背景技术Background technique
从生态环境的角度来看,磷石膏中含有氟、磷、硅等杂质,因磷石膏堆放,这一部分杂质经雨水冲刷容易污染地下水并破坏地质结构,因此,近年来,在科学处理磷石膏使其满足综合利用目标的处理方法的探索已经引起了社会研究机构的广泛关注。目前特定的预处理磷石膏的方法有水洗法、石灰中和法、煅烧法等,这些方法被广泛应用。虽然这些传统的处理方法能够满足磷石膏的可利用性,但在综合利用上仍然存在局限性,如水洗法耗水量大且磷石膏处理量不宜过多、煅烧法对燃料的要求较高、对磷石膏中杂质去除的程度小等。综上所述,有必要寻求一种能够有效去除磷石膏中杂质特别是杂质氟的方法。因此,为了解决磷石膏中杂质氟含量大的问题,迫切地需要寻找一种能够有效去除磷石膏中杂质氟并使其满足综合利用以及环保要求的工艺方法。From the perspective of the ecological environment, phosphogypsum contains impurities such as fluorine, phosphorus, and silicon. Due to the accumulation of phosphogypsum, this part of the impurities is likely to pollute groundwater and damage the geological structure after being washed by rainwater. Therefore, in recent years, in the scientific treatment of phosphogypsum The exploration of its processing methods to meet the comprehensive utilization goals has attracted widespread attention from social research institutions. At present, specific pretreatment methods of phosphogypsum include water washing method, lime neutralization method, calcination method, etc., and these methods are widely used. Although these traditional treatment methods can meet the availability of phosphogypsum, there are still limitations in the comprehensive utilization, such as the washing method consumes a lot of water and the amount of phosphogypsum should not be too much, the calcination method has higher requirements for fuel, and the The degree of removal of impurities in phosphogypsum is small and so on. In summary, it is necessary to find a method that can effectively remove impurities in phosphogypsum, especially the impurity fluorine. Therefore, in order to solve the problem of high impurity fluorine content in phosphogypsum, it is urgent to find a process that can effectively remove impurity fluorine in phosphogypsum and make it meet the requirements of comprehensive utilization and environmental protection.
据不完全统计,全球每年生产磷石膏2.12×104~2.97×104t,2015年,我国磷石膏堆存量已超过3×108t,磷石膏(Phosphogypsum,PG)是湿法磷酸厂和磷肥厂的主要固体废物,生产1t的磷酸大约产出4.5t~5t的磷石膏,磷石膏呈粉末状,主要成分是CaSO4·2H2O,磷石膏与天然石膏相比含有许多杂质,比如磷、氟、硅和有机物等。磷杂质对磷石膏综合利用特性影响最大,磷石膏本身具备的酸性特点,使其在我国华北、西北和东北地区被用作土壤改良剂,但这种磷石膏的资源利用并不能大规模的、从根本上的解决磷石膏的利用问题,而通过不同方法对磷石膏进行预处理可以有效改善其特性,使其能够更好地被利用,磷石膏中磷的影响最大,其次是氟和有机物,它们会对磷石膏的强度、水化率和白度等产生影响。磷石膏中还含有碱金属盐、硅、镁和放射性元素,如铀、镭等。磷主要存在于磷酸盐、碳酸盐等可溶性盐当中,会导致磷石膏制品在遇水时产生泛霜、粉化。硅主要以石英的形式存在,对磷石膏的性能影响较小。Fe2O3、Al2O3、MgO等有害杂质,对制备Ⅱ型无水石膏时胶结材料的水化和硬化有一定的促进作用,但它引入磷石膏中会影响二水石膏晶体的形貌。而磷石膏中又含有难以分离的放射性元素,对人体会产生危害。According to incomplete statistics, the annual production of phosphogypsum in the world is 2.12×10 4 ~2.97×10 4 t. In 2015, the stock of phosphogypsum in China has exceeded 3×10 8 t. Phosphogypsum (PG) is a wet process phosphoric acid plant and The main solid waste of the phosphate fertilizer plant, the production of 1 ton of phosphoric acid produces about 4.5t~5t of phosphogypsum. The phosphogypsum is in powder form and its main component is CaSO 4 2H 2 O. Compared with natural gypsum, phosphogypsum contains many impurities, such as Phosphorus, fluorine, silicon and organic matter, etc. Phosphorus impurities have the greatest impact on the comprehensive utilization characteristics of phosphogypsum. The acidic characteristics of phosphogypsum make it used as a soil amendment in North China, Northwest and Northeast China, but the resource utilization of this phosphogypsum cannot be used on a large scale. Fundamentally solve the utilization problem of phosphogypsum, and pretreatment of phosphogypsum by different methods can effectively improve its characteristics, so that it can be better utilized. Phosphorus in phosphogypsum has the greatest impact, followed by fluorine and organic matter. They will affect the strength, hydration rate and whiteness of phosphogypsum. Phosphogypsum also contains alkali metal salts, silicon, magnesium and radioactive elements such as uranium and radium. Phosphorus mainly exists in soluble salts such as phosphates and carbonates, which will cause phosphogypsum products to produce frost and pulverization when they meet water. Silicon mainly exists in the form of quartz and has little effect on the properties of phosphogypsum. Harmful impurities such as Fe 2 O 3 , Al 2 O 3 , and MgO can promote the hydration and hardening of cementing materials in the preparation of type II anhydrous gypsum, but their introduction into phosphogypsum will affect the shape of dihydrate gypsum crystals. appearance. And phosphogypsum contains radioactive elements that are difficult to separate, which will cause harm to the human body.
磷石膏是湿法生产磷酸的产物,近年来,国内磷石膏呈现出快速增长的态势,尤其在云南、贵州、湖北、安徽、四川、山东等磷矿大省产量较大,对磷石膏综合利用方面,美国、德国、日本、巴西等已经在该研究方面取得了成功,我国虽然对于磷石膏的综合利用研究起步比较晚,但是发展速度很快,经过多年的发展特别是科研院所和企业的科技攻关,磷石膏的应用在多个领域取得了较大发展。综合利用磷石膏不仅关系磷肥产业的经济、生态利益,也关系到环境保护和生态建设的发展,也符合循环经济、绿色发展的经济发展理念。到2015年底,中国磷石膏堆积量已超过3×108t,但其利用率较低(约10%左右)。Phosphogypsum is the product of phosphoric acid produced by wet process. In recent years, domestic phosphogypsum has shown a rapid growth trend, especially in Yunnan, Guizhou, Hubei, Anhui, Sichuan, Shandong and other provinces with large phosphate mines. Comprehensive utilization of phosphogypsum On the one hand, the United States, Germany, Japan, Brazil, etc. have achieved success in this research. Although my country’s research on the comprehensive utilization of phosphogypsum started relatively late, it has developed rapidly. After years of development, especially the research institutes and enterprises Scientific and technological research, the application of phosphogypsum has made great progress in many fields. The comprehensive utilization of phosphogypsum is not only related to the economic and ecological interests of the phosphate fertilizer industry, but also related to the development of environmental protection and ecological construction, and is also in line with the economic development concept of circular economy and green development. By the end of 2015, the accumulation of phosphogypsum in China had exceeded 3×10 8 t, but its utilization rate was low (about 10%).
硫酸是重要的基础化工原料,可以广泛应用于化肥、冶炼、火药、石化、农(医)药、军工业等行业。传统生产硫酸的原料是硫磺和硫铁矿,占硫酸总产量的70%,我国是一个硫资源贫乏的国家,每年都需要靠进口硫磺来满足需求,2008年进口硫磺1500t;水泥是社会建设的重要建筑材料,应用于土木建筑、水力、国防等工程中,生产水泥的主要原料为石灰石,生产中还会消耗大量的燃料和电力,并排放出大量的CO2和粉尘。Sulfuric acid is an important basic chemical raw material, which can be widely used in chemical fertilizer, smelting, gunpowder, petrochemical, agricultural (medical) medicine, military industry and other industries. The raw materials for the traditional production of sulfuric acid are sulfur and pyrite, which account for 70% of the total sulfuric acid production. China is a country with poor sulfur resources. Every year, it needs to rely on imported sulfur to meet the demand. In 2008, the imported sulfur was 1500t; cement is a social construction Important building materials, used in civil engineering, hydraulic, national defense and other projects. The main raw material for cement production is limestone. The production also consumes a lot of fuel and electricity, and emits a lot of CO 2 and dust.
我国每年在生产硫酸、水泥中需要进口硫磺、开采大量的矿产资源,这种行为不仅会占用外汇、快速消耗我国矿产资源,而且会对我国环境造成严重的污染。循环经济是时代发展的主题,但我国对硫酸和水泥的需求量却逐年上升,磷石膏的堆放问题亟待解决。利用磷石膏制酸联产水泥,不仅解决了硫资源和水泥的需求量,还避免了矿山开采和环境污染,一举多得,这将是磷石膏未来综合利用的一种有效途径。Every year in the production of sulfuric acid and cement, China needs to import sulfur and mine a large amount of mineral resources. This behavior will not only occupy foreign exchange and quickly consume my country's mineral resources, but also cause serious pollution to our environment. Circular economy is the theme of the development of the times, but my country's demand for sulfuric acid and cement is increasing year by year, and the problem of phosphogypsum stacking needs to be solved urgently. The use of phosphogypsum to produce acid and co-produce cement not only solves the demand for sulfur resources and cement, but also avoids mining and environmental pollution. This will serve multiple purposes. This will be an effective way for the comprehensive utilization of phosphogypsum in the future.
石膏制硫酸联产水泥的优点体现在,它是以石膏作为原料,将其分解为SO2和CaO,CaO和配制好的辅料在分解后直接煅烧成水泥熟料,然后和混合材料一起磨制成水泥产品,石膏中的其他杂质也被添入熟料中去,而含SO2的气体被制造成硫酸。一种原料可以生产两种产品,将利益扩大,同时无固废、废水排放,还可以替代传统的硫酸、水泥生产用原料,既减少了矿山开采,又减少了生产中的环境污染,但磷石膏中含氟量大,尤其是经过烘干工段烟气中时,含氟化物量较大,对设备的侵蚀程度较高。The advantage of co-production of cement from gypsum with sulfuric acid is that it uses gypsum as raw material and decomposes it into SO2 and CaO. CaO and the prepared auxiliary materials are directly calcined into cement clinker after decomposition, and then ground together with the mixed materials. into cement products, other impurities in gypsum are added to clinker, and SO 2 -containing gas is produced into sulfuric acid. One raw material can produce two kinds of products, which will expand the benefits. At the same time, there will be no solid waste and waste water discharge. It can also replace traditional raw materials for sulfuric acid and cement production, which not only reduces mining, but also reduces environmental pollution during production. However, phosphorus The fluorine content in gypsum is large, especially when it passes through the flue gas of the drying section, the fluoride content is relatively large, and the degree of corrosion to equipment is relatively high.
不同产地的磷石膏的化学组分含量略有不同,将来自贵州瓮安、安徽合肥、云南昆明的磷石膏样品均用密封性材料带回实验室,参考标准GB/T5484-2000、GB/T23456-2009、GC/T2073-2011对磷石膏样品进行研究分析,在120℃下对样品烘干2小时,冷却至室温后测定不同产地磷石膏化学组分含量,如表1。The chemical components of phosphogypsum from different origins are slightly different. The phosphogypsum samples from Weng'an, Guizhou, Hefei, Anhui, and Kunming, Yunnan were all brought back to the laboratory with sealing materials, and the reference standards GB/T5484-2000, GB/T23456 -2009, GC/T2073-2011 conducted research and analysis on phosphogypsum samples, dried the samples at 120°C for 2 hours, cooled to room temperature, and measured the chemical components of phosphogypsum from different origins, as shown in Table 1.
表1 不同产地磷石膏化学组分含量
目前,现有利用磷石膏的工艺都需对磷石膏进行预处理,在该厂磷石膏制酸联产水泥工艺中,磷石膏经过高温烟气烘干,氟杂质经过分解变成氟化物存在于烘干烟气当中,氟化物呈酸性,导致设备遭到腐蚀,所以一些研究者研究通过装置设备来去除磷石膏制酸烟气中的氟化物。At present, the existing processes using phosphogypsum require pretreatment of phosphogypsum. In the process of phosphogypsum acid production and co-production of cement in this plant, phosphogypsum is dried by high-temperature flue gas, and fluorine impurities are decomposed into fluoride and exist in the In the drying flue gas, the fluoride is acidic, which causes the equipment to be corroded, so some researchers have studied the removal of fluoride in the flue gas of phosphogypsum acid production by means of equipment.
王延军在公开发表的专利“一种磷石膏制硫酸烟气净化稀酸除氟装置”(CN205821060U)中介绍通过在待处理稀硫酸储槽后端连接除氟反应器,同时在除氟反应器入口设置除氟药剂管,将待处理稀硫酸与除氟药剂同时通入除氟反应器中,在除氟反应器中完成除氟工艺。除氟反应器的体积小、占地面积小,无需其他动力搅拌装置,反应在压力作用下通过压缩空气的作用使除氟药剂与稀酸充分均质反应,提高了反应速度,节省反应时间,进而提高氟的去除效率,在除氟反应器后端依次设置气浮沉降器、自动反洗表面过滤器和板框压滤机,对除氟后的滤液进一步净化处理,从而一次达到净化的目的,此装置结构简单、操作方便。但用设备装置对磷石膏制硫酸过程中烟气除氟不是解决磷石膏烟气含氟量高的根本之策,同时装置清洗困难,一旦发生故障会造成严重的氟泄露问题,存在安全和环境污染隐患。Wang Yanjun introduced in the published patent "a dilute acid defluorination device for sulfuric acid flue gas purification from phosphogypsum" (CN205821060U) that by connecting the defluorination reactor at the rear end of the dilute sulfuric acid storage tank to be treated, at the same time, at the entrance of the defluorination reactor Set up the fluoride removal agent pipe, pass the dilute sulfuric acid to be treated and the fluoride removal agent into the fluoride removal reactor at the same time, and complete the fluoride removal process in the fluoride removal reactor. The defluorination reactor has a small volume and a small footprint, and does not need other power stirring devices. Under the action of pressure, the defluorination agent and dilute acid are fully and homogeneously reacted by the action of compressed air, which improves the reaction speed and saves reaction time. In order to improve the removal efficiency of fluorine, an air flotation settler, an automatic backwash surface filter and a plate and frame filter press are arranged in sequence at the back end of the defluorination reactor to further purify the filtrate after defluorination, so as to achieve the purpose of purification at one time , This device is simple in structure and easy to operate. However, using equipment to remove fluorine from flue gas in the process of making sulfuric acid from phosphogypsum is not the fundamental solution to solve the high fluorine content of phosphogypsum flue gas. At the same time, it is difficult to clean the device. Once a failure occurs, it will cause serious fluorine leakage problems, which poses safety and environmental problems. Pollution hazard.
一些研究者选择在磷石膏进入烘干工段之前对其进行除氟预处理,主要方法包括水洗磷石膏去除氟等杂质、酸浸法除磷石膏中氟杂质和柠檬酸溶解去除杂质。同时酸洗法除磷石膏是先用硫酸溶液对磷石膏进行酸浸处理,然后经过过滤、水洗至中性,酸浸液返回到湿法磷酸工艺当中用作分解磷矿,水洗废液可以经过配酸循环用作磷石膏的浸取除杂,过程当中可以避免对环境造成二次污染。孔霞、李沪萍等发表的期刊“硫酸酸浸法除磷石膏中杂质氟的研究”中(化学工程, 2012,40(8):65-68)指出通过研究发现经过硫酸溶液热浸取的磷石膏中氟的去除率可以达到84.5%,含氟质量分数可以降低到0.0350%,得出较理想的优化实验条件是:浸取温度设置在88℃,浸取时间为45min,硫酸的质量分数为30%,含固量为0.43g/mL。经过这个方法处理的磷石膏提高了白度,大大扩大了磷石膏的利用率,此方法简单,效果好,不会造成二次污染。王宏等在期刊“浅述磷石膏水洗过滤工艺”中(贵州化工,2013,38(2):42-43)介绍了一种水洗过滤工艺可把磷石膏中的游离磷酸浓度控制在一定的范围内,作为原料供给生产硫酸铵装置使用,即解决磷石膏堆放污染问题,又起到循环利用促进经济的效果,为我国磷化工行业的进步及发展起到积极推动的作用。胡成军在期刊“磷石膏净化水洗试验及工艺”中(磷肥与复肥, 2007,22(5):66-67)利用水洗处理方法,去除磷石膏中杂质,从而使磷石膏能广泛用于纸面石膏板、石膏砌块等建材产品的生产,但这些研究均是水洗去除磷石膏中磷和可溶性磷及可溶性氟,对难溶性氟如CaF2、Na2SiF6、NaF等无法去除,同时对于水洗废液需要经过处理,不然会造成二次污染。苏联肥料和除虫杀菌科学研究所提出一种去除氟的方法,即温度在300℃对磷石膏热处理30min,酸度pH在1.8~2.2,湿度高于20%,则能去除废渣磷石膏中85~95%的氟,但上述方法所得废液显强酸性,处理不当会对环境造成污染。Some researchers choose to pre-treat phosphogypsum before it enters the drying section. The main methods include washing phosphogypsum to remove fluorine and other impurities, acid leaching to remove fluorine impurities in phosphogypsum, and citric acid to dissolve and remove impurities. At the same time, the pickling method to remove phosphogypsum is to first use sulfuric acid solution to pickle the phosphogypsum, then filter and wash to neutrality, and the pickling solution is returned to the wet phosphoric acid process to decompose phosphate rock, and the washing waste can be passed through The acid cycle is used for leaching and removing impurities of phosphogypsum, which can avoid secondary pollution to the environment during the process. Kong Xia, Li Huping, etc. published the journal "Studies on the Removal of Impurity Fluorine in Phosphorus Gypsum by Sulfuric Acid Leaching Method" (Chemical Engineering, 2012, 40 (8): 65-68), pointing out that the research found that after hot leaching of sulfuric acid solution The removal rate of fluorine in the phosphogypsum can reach 84.5%, and the mass fraction of fluorine can be reduced to 0.0350%. The ideal optimized experimental conditions are as follows: the leaching temperature is set at 88°C, the leaching time is 45min, the mass of sulfuric acid The fraction is 30%, and the solid content is 0.43g/mL. The whiteness of the phosphogypsum treated by this method is improved, and the utilization rate of the phosphogypsum is greatly expanded. The method is simple and effective, and will not cause secondary pollution. Wang Hong et al. introduced a water washing and filtering process to control the concentration of free phosphoric acid in phosphogypsum in the journal "Water Washing and Filtration Process of Phosphogypsum" (Guizhou Chemical Industry, 2013, 38 (2): 42-43). Within the scope, it is used as a raw material for the production of ammonium sulfate, which not only solves the pollution problem of phosphogypsum stacking, but also plays a role in promoting economy through recycling, and plays a positive role in promoting the progress and development of China's phosphorus chemical industry. In the journal "Phosphogypsum Purification and Washing Test and Technology" (Phosphate and Compound Fertilizer, 2007, 22 (5): 66-67), Hu Chengjun used the washing treatment method to remove impurities in phosphogypsum, so that phosphogypsum can be widely used in paper production of building materials such as gypsum boards, gypsum blocks, etc., but these studies are to remove phosphorus, soluble phosphorus and soluble fluorine in phosphogypsum by washing, and cannot remove insoluble fluorine such as CaF 2 , Na 2 SiF 6 , NaF, etc., and at the same time The washing waste liquid needs to be treated, otherwise it will cause secondary pollution. The Soviet Institute of Fertilizer, Pest Control and Sterilization Science proposed a method for removing fluorine, that is, heat-treating phosphogypsum at 300°C for 30 minutes, with an acidity pH of 1.8~2.2, and a humidity higher than 20%, it can remove 85~ 95% fluorine, but the waste liquid obtained by the above method is strongly acidic, and improper treatment will pollute the environment.
近年,我们公开了一种处理含锌废水吸附剂的制备方法及应用,其所述方法为对磷石膏进行氯化钠预处理后采用硫酸铝改性技术对磷石膏进行改性,制取得到铝基改性磷石膏吸附剂,Al3+通过离子交换反应进入到磷石膏层间,并使层间撑开以加大层间距和孔径,该吸附剂的微孔结构进一步增加,从而提高磷石膏的孔隙率和比表面积,具有良好的吸附性能,进一步处理后的磷石膏具有较高的吸附容量,使之能够成为一种去除锌离子的优良吸附材料(CN201410690082.7),羟基磷灰石(HA)对F–具有强大的吸附作用,但普通方法合成的HA吸附性较差,我们报道了一种合成纳米到微米级的羟基磷灰石(HA)的新方法,这种方法可以有效提高HA过滤器对F–的吸附效率(Environmental Science & Technology,2014,48(10):5798),之后,对水泥厂磷石膏废渣处理做了一些完善,磷石膏的直接碳水化,使其在钙循环过程中所获得的碳酸化产品可用于CO2的捕集,并利用废CaO基吸附剂制造水泥熟料,而水泥厂烟气中衍生的CO2可直接将在磷石膏中的硫酸钙转化为碳酸钙,因此,运用此法不仅可以回收磷石膏废渣,而且可以减少水泥厂的CO2排放(Energy & Fuels,2016,30(2)),对磷石膏的回收,我们通过以高硫煤为还原剂,采用热重分析、差热分析、扫描电镜、X射线衍射等手段对不同气氛条件下磷石膏在氮气气氛中的分解过程进行了表征,其主要产物为硫铝酸钙(Industrial & Engineering Chemistry Research, 2010,49(8):3597-3602),在“湿法磷酸法”化肥生产中,磷石膏属于一种废物副产物,但磷石膏在其它领域中却大有用途,所以对其的回收就显得尤为重要,我们报道了一种对磷石膏的分解回收方法,其中还原剂为CO,添加剂为氯化钙,分解温度为790℃,其主要产物为硫铝酸钙,但此方法中使用还原剂为CO,属有毒气体,易对人体产生危害(Industrial & Engineering Chemistry Research, 2012,51(19):6680–6685),稀土元素的全球需求量正在迅速增加,而磷酸生产的副产品磷石膏被认为是稀土元素的来源之一,我们报道了在浸出溶液中添加硫酸钙硬石膏种子,从而抑制浸出液中硫酸钙的降解并使钙浓度降低,而稀土的浸出效率又与磷石膏溶解度有关,即其浓度下降可增加稀土元素浸出量(Industrial & Engineering Chemistry Research, 2016,55,12309-12316)。In recent years, we have disclosed a preparation method and application of an adsorbent for treating zinc-containing wastewater. The method is to modify the phosphogypsum by using aluminum sulfate modification technology after pretreatment with sodium chloride to obtain Aluminum-based modified phosphogypsum adsorbent, Al 3+ enters the interlayer of phosphogypsum through ion exchange reaction, and makes the interlayer open to increase the interlayer distance and pore size, the microporous structure of the adsorbent is further increased, thereby improving the phosphorus The porosity and specific surface area of gypsum have good adsorption performance, and the further processed phosphogypsum has a high adsorption capacity, making it an excellent adsorption material for removing zinc ions (CN201410690082.7), hydroxyapatite (HA) has a strong adsorption effect on F- , but the adsorption of HA synthesized by common methods is poor. We report a new method for the synthesis of nano- to micro-sized hydroxyapatite (HA), which can effectively Improve the adsorption efficiency of HA filter to F – ( Environmental Science & Technology , 2014, 48 (10): 5798), after that, some improvements were made to the treatment of phosphogypsum waste residue in cement plants, and the direct carbonation of phosphogypsum made it in Carbonation products obtained during the calcium cycle can be used for CO2 capture and the use of spent CaO-based sorbents to manufacture cement clinker, while CO2 derived from cement plant flue gas can directly convert calcium sulfate in phosphogypsum Therefore, this method can not only recycle phosphogypsum waste residue, but also reduce CO 2 emissions from cement plants ( Energy & Fuels , 2016, 30 (2)). For the recovery of phosphogypsum, we use high-sulfur gypsum Coal was used as the reducing agent. The decomposition process of phosphogypsum in nitrogen atmosphere under different atmospheric conditions was characterized by means of thermogravimetric analysis, differential thermal analysis, scanning electron microscopy, and X-ray diffraction. The main product was calcium sulfoaluminate ( Industrial & Engineering Chemistry Research , 2010, 49 (8):3597-3602), in the "wet process phosphoric acid method" fertilizer production, phosphogypsum is a waste by-product, but phosphogypsum is very useful in other fields, so Its recovery is particularly important. We reported a method for the decomposition and recovery of phosphogypsum, in which the reducing agent is CO, the additive is calcium chloride, the decomposition temperature is 790 °C, and the main product is calcium sulfoaluminate. The reducing agent used in this method is CO, which is a toxic gas and is easy to cause harm to the human body ( Industrial & Engineering Chemistry Research , 2012, 51 (19):6680–6685). The global demand for rare earth elements is increasing rapidly, and phosphoric acid production The by-product of phosphogypsum is considered to be one of the sources of rare earth elements, and we report that the addition of calcium sulfate anhydrite seeds to the leach solution inhibits the degradation of calcium sulfate in the leach solution And reduce the calcium concentration, and the leaching efficiency of rare earth is related to the solubility of phosphogypsum, that is, the decrease of its concentration can increase the leaching amount of rare earth elements ( Industrial & Engineering Chemistry Research , 2016, 55 , 12309-12316).
经过文献调研,从除氟效果、环境污染、经济成本、技术难度等方面对三种去除磷石膏中氟杂质方法进行比较,并根据研究地的磷石膏的主要特性,采用柠檬酸溶液溶解加水洗的方法对磷石膏预处理,达到去除磷石膏中氟杂质的目的。柠檬酸用途非常广泛,用于食品、化工、医药行业,食品行业主要用作酸味剂和防腐剂,化工行业利用柠檬酸作络合剂和缓冲溶液,医药业主要用柠檬酸作枸橼酸根离子,其与钙离子能形成一种难以解离的可溶性络合物,因而降低了血中钙离子浓度,使血液凝固受阻,是很好的体外抗凝药。柠檬酸与磷石膏中各类杂质反应生成大量水溶性成分,与氟化物的反应方程式为:After literature research, three methods for removing fluorine impurities in phosphogypsum were compared from the aspects of fluoride removal effect, environmental pollution, economic cost, and technical difficulty. The method is used to pretreat phosphogypsum to achieve the purpose of removing fluorine impurities in phosphogypsum. Citric acid is widely used in food, chemical, and pharmaceutical industries. The food industry is mainly used as a sour agent and preservative. The chemical industry uses citric acid as a complexing agent and buffer solution. The pharmaceutical industry mainly uses citric acid as citrate ions. , It can form a soluble complex with calcium ions that is difficult to dissociate, thus reducing the concentration of calcium ions in the blood and hindering blood coagulation. It is a good anticoagulant in vitro. Citric acid reacts with various impurities in phosphogypsum to generate a large amount of water-soluble components, and the reaction equation with fluoride is:
2C6H8O7+3NaF→Na3(C6H5O7)2+3HF2C 6 H 8 O 7 +3NaF→Na 3 (C 6 H 5 O 7 ) 2 +3HF
4C6H8O7+3Na2SiF6→2Na3(C6H5O7)2+H3SiF6 4C 6 H 8 O 7 +3Na 2 SiF 6 →2Na 3 (C 6 H 5 O 7 ) 2 +H 3 SiF 6
2C6H8O7+2Na3AlF6→2Na3(C6H5O7)2+H3AlF6 2C 6 H 8 O 7 +2Na 3 AlF 6 →2Na 3 (C 6 H 5 O 7 ) 2 +H 3 AlF 6
2C6H8O7+3Na2FeF6→2Na3(C6H5O7)2+H3FeF6 2C 6 H 8 O 7 +3Na 2 FeF 6 →2Na 3 (C 6 H 5 O 7 ) 2 +H 3 FeF 6
2C6H8O7+3CaF2→Ca3(C6H5O7)2+6HF2C 6 H 8 O 7 +3CaF 2 →Ca 3 (C 6 H 5 O 7 ) 2 +6HF
与磷酸盐反应方程式为:The reaction equation with phosphate is:
2C6H8O7+3Ca(H2PO4)2·H2O→Ca3(C6H5O7)2+2H3PO4 2C 6 H 8 O 7 +3Ca(H 2 PO 4 ) 2 ·H 2 O→Ca 3 (C 6 H 5 O 7 ) 2 +2H 3 PO 4
2C6H8O7+3CaHPO4·2H2O→Ca3(C6H5O7)2+2H3PO4+2H2O2C 6 H 8 O 7 +3CaHPO 4 2H 2 O→Ca 3 (C 6 H 5 O 7 ) 2 +2H 3 PO 4 +2H 2 O
2C6H8O7+Ca3(PO4)2→Ca3(C6H5O7)2+2H3PO4 2C 6 H 8 O 7 +Ca 3 (PO 4 ) 2 →Ca 3 (C 6 H 5 O 7 ) 2 +2H 3 PO 4
由上述柠檬酸与磷石膏的反应可知,柠檬酸可与磷石膏中的磷酸盐和氟化物反应生成可被水洗的易溶物质,通过水洗可以达到除杂的效果。From the above reaction between citric acid and phosphogypsum, it can be seen that citric acid can react with phosphate and fluoride in phosphogypsum to form easily soluble substances that can be washed with water, and the effect of removing impurities can be achieved by washing with water.
在本发明中,我们报道了以柠檬酸作为溶解剂来纯化磷石膏并结合水洗来去除磷石膏中杂质氟的方法。In the present invention, we report a method of purifying phosphogypsum with citric acid as a dissolving agent, combined with water washing to remove impurity fluorine in phosphogypsum.
近年来,固体废物磷石膏的综合利用研究引起了各方专家学者的兴趣。在“硫酸生产现状及磷石膏制硫酸研究进展”中廖秋实、覃明武等人(湖北三峡职业技术学院学报,2015, (1):98-100)介绍了硫磺制酸、磷石膏制酸等工艺的优缺点以及磷石膏综合利用的现状。2013年李继升等人公开了发明专利(CN201310475824.X)“磷石膏的洗涤净化方法”的制备方法。它采用了下述步骤:将磷石膏放入水中,进行水洗,去除其中的细小可溶性杂质,之后进入阶梯池进行分级洗涤,阶梯池分为2-5级,去除磷石膏中细小的不溶性杂质,再进行湿筛过滤,除去磷石膏中大颗粒的石英和未反应的杂质,最后采用石灰进行中和,去除磷石膏中残留的酸。2015年曹志强等人公开了发明专利(CN201520404286.X)“一种去除磷石膏中有机物的装置”的使用方法。该方法主要阐述了一种去除磷石膏中有机物的装置,通过气浮重力法将磷石膏料浆中有机物随气泡带到分离锥罐上部的环形溢流槽内溢出收集,分离锥罐内的剩余料浆通过清洗装置清洗后在出料口收集。2016年Merka等人公开了发明专利(WO2016186527)“Method for complex treatment of phosphogypsum”的制备方法。它采用了下述步骤:将磷石膏与硫酸溶液反应后,所得混合物分离成液体和沉积物,沉积物主要含有硫酸钙,将沉积物与氨水和CO2反应后生成硫酸铵和碳酸钙,过滤干燥后将所得沉淀碳酸钙溶解于硝酸中,再将所得混合物分离,得到硝酸盐溶液和氟化物沉淀以及硅酸盐沉淀。2017年Konstantin Kovler等人公开了发明专利(US20170022070)“System andmethods for removing impurities from phosphogypsum and manufacturing gypsumbinders and products”的制备方法。它采用了下述步骤:将磷石膏在酸性环境下与氯化物溶液反应,获得磷石膏沉淀物,经脱水过滤后利用电化学和沸石吸附以除去磷石膏中所含杂质。2017年EогатыреваЕленаВладимировна等人公开了发明专利(RU0002607862)“Method of extracting rare-earth metals and producing gypsum plaster fromanhydrite”的制备方法。该方法主要阐述了一种从磷灰石制酸生产硫酸的废渣中获得稀土金属和磷石膏建筑石膏的方法。In recent years, the comprehensive utilization of solid waste phosphogypsum has aroused the interest of experts and scholars from all walks of life. Liao Qiushi, Qin Mingwu et al. (Journal of Hubei Three Gorges Vocational and Technical College, 2015, (1): 98-100) introduced the processes of sulfuric acid production and phosphogypsum production Advantages and disadvantages and the current situation of comprehensive utilization of phosphogypsum. In 2013, Li Jisheng and others disclosed the preparation method of the invention patent (CN201310475824.X) "Washing and purification method of phosphogypsum". It adopts the following steps: put the phosphogypsum into the water, wash it with water, remove the fine soluble impurities, and then enter the stepped pool for graded washing. The stepped pool is divided into 2-5 levels to remove the fine insoluble impurities in the phosphogypsum. Then carry out wet sieve filtration to remove large particles of quartz and unreacted impurities in the phosphogypsum, and finally neutralize with lime to remove the residual acid in the phosphogypsum. In 2015, Cao Zhiqiang and others disclosed the use method of the invention patent (CN201520404286.X) "a device for removing organic matter in phosphogypsum". This method mainly describes a device for removing organic matter in phosphogypsum. The organic matter in the phosphogypsum slurry is brought to the ring-shaped overflow tank on the upper part of the separation cone tank by the air flotation gravity method to overflow and collect the organic matter in the separation cone tank. After the slurry is cleaned by the cleaning device, it is collected at the discharge port. In 2016, Merka et al. disclosed the preparation method of the invention patent (WO2016186527) "Method for complex treatment of phosphogypsum". It uses the following steps: after reacting phosphogypsum with sulfuric acid solution, the resulting mixture is separated into a liquid and a sediment, the sediment mainly contains calcium sulfate, the sediment is reacted with ammonia and CO2 to form ammonium sulfate and calcium carbonate, filtered After drying, the resulting precipitated calcium carbonate is dissolved in nitric acid, and the resulting mixture is separated to obtain a nitrate solution and a fluoride precipitate and a silicate precipitate. In 2017, Konstantin Kovler et al. disclosed the preparation method of the invention patent (US20170022070) "System and methods for removing impurities from phosphogypsum and manufacturing gypsumbinders and products". It adopts the following steps: react phosphogypsum with chloride solution in an acidic environment to obtain phosphogypsum precipitates, dehydrate and filter, and use electrochemical and zeolite adsorption to remove impurities contained in the phosphogypsum. In 2017, Eогатырева Елена Владимировна and others disclosed the preparation method of the invention patent (RU0002607862) "Method of extracting rare-earth metals and producing gypsum plaster from anhydrate". The method mainly describes a method for obtaining rare earth metals and phosphogypsum building gypsum from the waste residue of apatite acid production and sulfuric acid production.
上述方法虽有诸多优点,但其部分方法中所涉及方法实际运作难度大,且对氟含量处理不够彻底,针对性差,不能从根本上解决问题,而柠檬酸加水洗工艺不仅可以对磷石膏进行预处理,且对磷石膏中所含氟及难溶性氟的针对性强,去除率高,后续水洗废水经处理可循环使用。Although the above methods have many advantages, some of the methods involved in the methods are difficult to operate in practice, and the treatment of fluorine content is not thorough enough, the pertinence is poor, and the problem cannot be fundamentally solved. Pretreatment, and the fluorine contained in phosphogypsum and insoluble fluorine are highly targeted, and the removal rate is high, and the subsequent washing wastewater can be recycled after treatment.
发明内容Contents of the invention
发明目的:针对目前现有技术存在的不足之处,本发明利用柠檬酸对磷石膏中杂质成分溶解程度的不同,来实现将磷石膏中氟化物等杂质的转化为可溶性水洗杂质,并结合水洗方法,设计出一种对磷石膏中氟杂质的柠檬酸加水洗去除工艺。此方法通过对比不同浓度柠檬酸溶解加水洗对磷石膏中杂质氟去除率的不同,寻找一种有效的对磷石膏预处理使其符合磷石膏制酸联产水泥工艺标准的方法。Purpose of the invention: Aiming at the deficiencies of the current prior art, the present invention utilizes the difference in solubility of impurity components in phosphogypsum by citric acid to realize the conversion of impurities such as fluoride in phosphogypsum into soluble water-washable impurities, and combined with water-washing Methods, a process for removing fluorine impurities in phosphogypsum by washing with citric acid and water was designed. In this method, by comparing the removal rate of impurity fluorine in phosphogypsum by dissolving with different concentrations of citric acid and washing with water, an effective method for pretreatment of phosphogypsum to make it meet the process standard of phosphogypsum acid production co-production cement is found.
本发明的技术方案是:一种用于去除磷石膏中杂质氟的柠檬酸加水洗的工艺方法,包括柠檬酸溶解、柠檬酸洗涤和水洗三道工序。其特征在于:所述柠檬酸溶液可与磷石膏中杂质发生化学作用,使磷石膏中氟化物和磷酸盐等杂质转化成可水洗的易溶性物质,再通过水洗工艺进行除杂,使净化后的磷石膏能更好的被磷石膏制酸联产水泥工艺利用,从而降低烘干烟气中氟化物含量,同时不影响硫酸和水泥生产工艺,所述的柠檬酸加水洗的工艺方法的制备过程包括如下三个步骤:The technical proposal of the present invention is: a process method for removing impurity fluorine in phosphogypsum by adding citric acid and water washing, including three processes of citric acid dissolution, citric acid washing and water washing. It is characterized in that: the citric acid solution can chemically react with impurities in phosphogypsum, so that impurities such as fluoride and phosphate in phosphogypsum can be converted into water-washable and easily soluble substances, and then impurities can be removed by water washing process, so that after purification The phosphogypsum can be better utilized by the phosphogypsum acid production co-production cement process, thereby reducing the fluoride content in the drying flue gas, and does not affect the sulfuric acid and cement production process at the same time, the preparation of the process method of adding citric acid and water washing The process consists of three steps:
1.1第一步是配制不同浓度柠檬酸溶液:用精度为百分之一的电子天平分别准确称取柠檬酸3.00g、4.00g、5.00g、6.00g和7.00g,分别配比质量浓度为3%、4%、5%、6%和7%的柠檬酸水溶液备用,再从上述配制好的柠檬酸水溶液中分别量取10mL置于150mL烧杯中,各加入90mL去离子水,将其稀释为质量浓度为0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液备用;1.1 The first step is to prepare different concentrations of citric acid solutions: accurately weigh 3.00g, 4.00g, 5.00g, 6.00g and 7.00g of citric acid with an electronic balance with an accuracy of 1%, and the proportioning mass concentration is 3 %, 4%, 5%, 6% and 7% citric acid aqueous solution for later use, then measure 10mL from the above-mentioned prepared citric acid aqueous solution and place it in a 150mL beaker, add 90mL deionized water each, and dilute it to The citric acid aqueous solution that mass concentration is 0.3%, 0.4%, 0.5%, 0.6% and 0.7% is standby;
1.2第二步是用柠檬酸加水洗处理磷石膏:用精度为百分之一的电子天平称取9.00g~9.60g的磷石膏原料样品六份,分别置于相同刻度与大小的玻璃器皿中,再分别取10mL的3%、4%、5%、6%和7%的柠檬酸水溶液加入到磷石膏样品中,机械搅拌15~25min直至溶解,溶解后的混合物经过过滤装置过滤,滤液移至收集槽收集,用质量浓度0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液对过滤后的滤渣进行超声分散洗涤6~10min,并在离心机中以3000~4000rpm转速离心8~12min,然后加入纯水超声分散洗涤并旋转离心2次,离心后得到的净化后磷石膏样品1#、2#、3#、4#、5#,再将净化后的磷石膏样品经过85℃的电热恒温鼓风干燥箱内干燥12h,得到成品;1.2 The second step is to wash the phosphogypsum with citric acid and water: use an electronic balance with an accuracy of 1% to weigh six samples of phosphogypsum raw materials of 9.00g~9.60g, and place them in glassware with the same scale and size. , and then take 10mL of 3%, 4%, 5%, 6% and 7% citric acid aqueous solution into the phosphogypsum sample, stir mechanically for 15~25min until dissolved, the dissolved mixture is filtered through the filter device, and the filtrate is pipetted To the collection tank for collection, the filtered filter residue was ultrasonically dispersed and washed with citric acid aqueous solutions with a mass concentration of 0.3%, 0.4%, 0.5%, 0.6% and 0.7% for 6-10 minutes, and centrifuged in a centrifuge at a speed of 3000-4000rpm 8~12min, then add pure water to ultrasonically disperse and wash and rotate and centrifuge twice, the purified phosphogypsum samples 1 # , 2 # , 3 # , 4 # , 5 # obtained after centrifugation, and then the purified phosphogypsum samples are passed through Dry in an electric heating constant temperature blast drying oven at 85°C for 12 hours to obtain the finished product;
1.3第三步是石灰中和处理水洗废水:配比质量浓度为0.3~0.5%的石灰水加入到废液收集槽中,搅拌8~12min,得到均匀料浆,用pH计测定料浆的pH值,并加入质量浓度为85~95%的石灰水将此料浆的pH值调节至7;最后加入明矾溶液,在废水处理槽内搅拌10~15min后静置分层,得到上层pH值为7的中和水和下层难溶的沉淀物。1.3 The third step is lime neutralization and treatment of washing wastewater: add lime water with a mass concentration of 0.3~0.5% into the waste liquid collection tank, stir for 8~12 minutes to obtain a uniform slurry, and use a pH meter to measure the pH of the slurry value, and add lime water with a mass concentration of 85-95% to adjust the pH value of the slurry to 7; finally add alum solution, stir in the wastewater treatment tank for 10-15 minutes, and then let it stand for stratification to obtain the pH value of the upper layer 7. Neutralize the water and the insoluble sediment in the lower layer.
作为对现有技术的进一步改进,所说利用柠檬酸加水洗处理磷石膏来达到除氟效果的方法,磷石膏除氟过程中除了添加柠檬酸以外没有添加其他酸碱性添加剂。所说的磷石膏为磷酸厂湿法生产的固体废物。所说的磷石膏除氟是相对于未经过处理的磷石膏氟含量的相对去除率。所说的柠檬酸加水洗去除磷石膏中氟杂质,工艺操作简单、经济成本合理、生产周期短。所说的磷石膏原料来源丰富、成本低、易获得。所说的除氟后磷石膏用作磷石膏制酸联产水泥工艺原料,能够使磷石膏在烘干工段产生的烟气中氟化物减少,避免设备侵蚀,具有一定的环保意义。As a further improvement to the prior art, the method of using citric acid plus water to wash phosphogypsum to achieve the effect of fluoride removal does not add other acid-base additives except citric acid in the process of phosphogypsum defluoridation. The said phosphogypsum is the solid waste produced by the wet method of the phosphoric acid plant. The said phosphogypsum removal of fluoride is the relative removal rate relative to the fluorine content of untreated phosphogypsum. The citric acid is washed with water to remove the fluorine impurities in the phosphogypsum, and the process operation is simple, the economic cost is reasonable, and the production cycle is short. Said phosphogypsum raw material is rich in sources, low in cost and easy to obtain. The defluoridated phosphogypsum is used as a raw material for the co-production of cement with phosphogypsum acid, which can reduce the fluoride in the flue gas generated by the phosphogypsum in the drying section and avoid equipment erosion, which has certain environmental protection significance.
相对于现有技术的有益效果:Compared with the beneficial effects of the prior art:
近年来,固体废物磷石膏的综合利用研究引起了各方专家学者的兴趣。在“硫酸生产现状及磷石膏制硫酸研究进展”中廖秋实、覃明武等人(湖北三峡职业技术学院学报,2015,(1):98-100)介绍了硫磺制酸、磷石膏制酸等工艺的优缺点以及磷石膏综合利用的现状。2013年李继升等人公开了发明专利(CN201310475824.X)“磷石膏的洗涤净化方法”的制备方法。它采用了下述步骤:将磷石膏放入水中,进行水洗,去除其中的细小可溶性杂质,之后进入阶梯池进行分级洗涤,阶梯池分为2-5级,去除磷石膏中细小的不溶性杂质,再进行湿筛过滤,除去磷石膏中大颗粒的石英和未反应的杂质,最后采用石灰进行中和,去除磷石膏中残留的酸。2015年曹志强等人公开了发明专利(CN201520404286.X)“一种去除磷石膏中有机物的装置”的制备方法。该方法主要阐述了一种去除磷石膏中有机物的装置,通过气浮重力法将磷石膏料浆中有机物随气泡带到分离锥罐上部的环形溢流槽内溢出收集,分离锥罐内的剩余料浆通过清洗装置清洗后在出料口收集。2016年Merka等人公开了发明专利(WO2016186527)“Method for complex treatment of phosphogypsum”的制备方法。它采用了下述步骤:将磷石膏与硫酸溶液反应后,所得混合物分离成液体和沉积物,沉积物主要含有硫酸钙,将沉积物与氨水和CO2反应后生成硫酸铵和碳酸钙,过滤干燥后将所得沉淀碳酸钙溶解于硝酸中,再将所得混合物分离,得到硝酸盐溶液和氟化物沉淀以及硅酸盐沉淀。2017年Konstantin Kovler等人公开了发明专利(US20170022070)“System and methodsfor removing impurities from phosphogypsum and manufacturing gypsum bindersand products”的制备方法。它采用了下述步骤:将磷石膏在酸性环境下与氯化物溶液反应,获得磷石膏沉淀物,经脱水过滤后利用电化学和沸石吸附以除去磷石膏中所含杂质。2017年EогатыреваЕленаВладимировна等人公开了发明专利(RU0002607862)“Method of extracting rare-earth metals and producing gypsum plaster fromanhydrite”的制备方法。该方法主要阐述了一种从磷灰石制酸生产硫酸的废渣中获得稀土金属和磷石膏建筑石膏的方法。In recent years, the comprehensive utilization of solid waste phosphogypsum has aroused the interest of experts and scholars from all walks of life. Liao Qiushi, Qin Mingwu et al. (Journal of Hubei Three Gorges Vocational and Technical College, 2015, (1): 98-100) introduced the processes of sulfuric acid production and phosphogypsum production Advantages and disadvantages and the current situation of comprehensive utilization of phosphogypsum. In 2013, Li Jisheng and others disclosed the preparation method of the invention patent (CN201310475824.X) "Washing and purification method of phosphogypsum". It adopts the following steps: put the phosphogypsum into the water, wash it with water, remove the fine soluble impurities, and then enter the stepped pool for graded washing. The stepped pool is divided into 2-5 levels to remove the fine insoluble impurities in the phosphogypsum. Then carry out wet sieve filtration to remove large particles of quartz and unreacted impurities in the phosphogypsum, and finally neutralize with lime to remove the residual acid in the phosphogypsum. In 2015, Cao Zhiqiang and others disclosed the preparation method of the invention patent (CN201520404286.X) "a device for removing organic matter in phosphogypsum". This method mainly describes a device for removing organic matter in phosphogypsum. The organic matter in the phosphogypsum slurry is brought to the ring-shaped overflow tank on the upper part of the separation cone tank by the air flotation gravity method to overflow and collect the organic matter in the separation cone tank. After the slurry is cleaned by the cleaning device, it is collected at the discharge port. In 2016, Merka et al. disclosed the preparation method of the invention patent (WO2016186527) "Method for complex treatment of phosphogypsum". It uses the following steps: after reacting phosphogypsum with sulfuric acid solution, the resulting mixture is separated into a liquid and a sediment, the sediment mainly contains calcium sulfate, the sediment is reacted with ammonia and CO2 to form ammonium sulfate and calcium carbonate, filtered After drying, the resulting precipitated calcium carbonate is dissolved in nitric acid, and the resulting mixture is separated to obtain a nitrate solution and a fluoride precipitate and a silicate precipitate. In 2017, Konstantin Kovler et al. disclosed the preparation method of the invention patent (US20170022070) "System and methods for removing impurities from phosphogypsum and manufacturing gypsum binders and products". It adopts the following steps: react phosphogypsum with chloride solution in an acidic environment to obtain phosphogypsum precipitates, dehydrate and filter, and use electrochemical and zeolite adsorption to remove impurities contained in the phosphogypsum. In 2017, Eогатырева Елена Владимировна and others disclosed the preparation method of the invention patent (RU0002607862) "Method of extracting rare-earth metals and producing gypsum plaster from anhydrate". The method mainly describes a method for obtaining rare earth metals and phosphogypsum building gypsum from the waste residue of apatite acid production and sulfuric acid production.
上述方法虽有诸多优点,但其部分方法中所涉及方法实际运作难度大,且对氟含量处理不够彻底,针对性差,不能从根本上解决问题,而柠檬酸加水洗工艺不仅可以对磷石膏进行预处理,且对磷石膏中所含氟及难溶性氟的针对性强,去除率高,后续水洗废水经处理可循环使用。Although the above methods have many advantages, some of the methods involved in the methods are difficult to operate in practice, and the treatment of fluorine content is not thorough enough, the pertinence is poor, and the problem cannot be fundamentally solved. Pretreatment, and the fluorine contained in phosphogypsum and insoluble fluorine are highly targeted, and the removal rate is high, and the subsequent washing wastewater can be recycled after treatment.
本发明首先是配制不同浓度柠檬酸溶液:用精度为百分之一的电子天平分别准确称取柠檬酸3.00g、4.00g、5.00g、6.00g和7.00g,分别配比质量浓度为3%、4%、5%、6%和7%的柠檬酸水溶液备用,再从上述配制好的柠檬酸水溶液中分别量取10mL置于150mL烧杯中,各加入90mL去离子水,将其稀释为质量浓度为0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液备用;The present invention first prepares citric acid solutions with different concentrations: accurately weigh 3.00g, 4.00g, 5.00g, 6.00g and 7.00g of citric acid respectively with an electronic balance with an accuracy of 1%, and the proportioning mass concentration is 3% respectively , 4%, 5%, 6% and 7% citric acid aqueous solutions for later use, then measure 10mL from the above prepared citric acid aqueous solution and place them in 150mL beakers, add 90mL deionized water each, and dilute it to mass Concentration is the citric acid aqueous solution of 0.3%, 0.4%, 0.5%, 0.6% and 0.7% standby;
其次是用柠檬酸加水洗处理磷石膏:用精度为百分之一的电子天平称取9.00g~9.60g的磷石膏原料样品六份,分别置于相同刻度与大小的玻璃器皿中,再分别取10mL的3%、4%、5%、6%和7%的柠檬酸水溶液加入到磷石膏样品中,机械搅拌15~25min直至溶解,溶解后的混合物经过过滤装置过滤,滤液移至收集槽收集,用质量浓度0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液对过滤后的滤渣进行超声分散洗涤6~10min,并在离心机中以3000~4000rpm转速离心8~12min,然后加入纯水超声分散洗涤并旋转离心2次,离心后得到的净化后磷石膏样品1#、2#、3#、4#、5#,再将净化后的磷石膏样品经过85℃的电热恒温鼓风干燥箱内干燥12h,得到成品;The second is to wash the phosphogypsum with citric acid and water: use an electronic balance with an accuracy of 1% to weigh six samples of phosphogypsum raw materials of 9.00g~9.60g, place them in glassware with the same scale and size, and then weigh them separately. Take 10mL of 3%, 4%, 5%, 6% and 7% citric acid aqueous solution and add it to the phosphogypsum sample, stir mechanically for 15~25min until dissolved, the dissolved mixture is filtered through the filter device, and the filtrate is moved to the collection tank Collect, use citric acid aqueous solution with mass concentration of 0.3%, 0.4%, 0.5%, 0.6% and 0.7% to ultrasonically disperse and wash the filtered filter residue for 6~10min, and centrifuge at 3000~4000rpm in a centrifuge for 8~12min , and then add pure water to ultrasonically disperse and wash and rotate and centrifuge twice. After centrifugation, the purified phosphogypsum samples 1 # , 2 # , 3 # , 4 # , 5 # are subjected to a temperature of 85 ° C. Dry in an electric heating constant temperature blast drying oven for 12 hours to obtain the finished product;
最后是石灰中和处理水洗废水:配比质量浓度为0.3~0.5%的石灰水加入到废液收集槽中,搅拌8~12min,得到均匀料浆,用pH计测定料浆的pH值,并加入质量浓度为85~95%的石灰水将此料浆的pH值调节至7;最后加入明矾溶液,在废水处理槽内搅拌10~15min后静置分层,得到上层pH值为7的中和水和下层难溶的沉淀物。Finally, lime is neutralized to treat washing wastewater: lime water with a mass concentration of 0.3-0.5% is added to the waste liquid collection tank, stirred for 8-12 minutes to obtain a uniform slurry, and the pH value of the slurry is measured with a pH meter, and Add lime water with a mass concentration of 85-95% to adjust the pH value of the slurry to 7; finally add alum solution, stir in the wastewater treatment tank for 10-15 minutes, and then let it stand for stratification to obtain a medium with a pH value of 7 in the upper layer. and water and insoluble precipitates in the lower layer.
综上所述,一种用于去除磷石膏中杂质氟的柠檬酸加水洗的工艺方法具有以下优点:In summary, a process of washing with citric acid for removing impurity fluorine in phosphogypsum has the following advantages:
其一: 用柠檬酸加水洗方法来处理湿法磷酸固体废物磷石膏,可以使磷石膏中的氟杂质得到明显去除。One: The wet-process phosphoric acid solid waste phosphogypsum is treated with citric acid plus water washing, which can significantly remove the fluorine impurities in the phosphogypsum.
其二:经过柠檬酸加水洗处理后的磷石膏中主要成分没有发生改变,不影响磷石膏制酸联产水泥工艺的进行。Second: the main components of the phosphogypsum after washing with citric acid and water have not changed, which does not affect the process of producing acid and co-producing cement from phosphogypsum.
其三:磷石膏是湿法磷酸的主要固体废物,其生产量、堆积量在逐年增加,由于杂质成分多易造成环境污染的问题,经过预处理后的磷石膏作为原料更符合综合利用的特点,具有一定环保意义。Third: Phosphogypsum is the main solid waste of wet-process phosphoric acid, and its production volume and accumulation are increasing year by year. Due to the large amount of impurities, it is easy to cause environmental pollution. The pretreated phosphogypsum as a raw material is more in line with the characteristics of comprehensive utilization , has a certain environmental significance.
其四:柠檬酸加水洗废液经过收集使用明矾与石灰中和方法处理,得到的中性水可以用于工艺循环使用。Fourth: the citric acid plus water washing waste liquid is collected and treated with alum and lime neutralization method, and the obtained neutral water can be used for process recycling.
其五:与其他磷石膏除氟方法比较,具有操作简单、投资成本低、易于实现且氟杂质去除效果好的特点。Fifth: Compared with other phosphogypsum defluorination methods, it has the characteristics of simple operation, low investment cost, easy implementation and good fluorine impurity removal effect.
其六:处理后磷石膏作为磷石膏制酸联产水泥工艺中原料,由于氟含量降低,使烘干烟气中氟化物含量相对降低,设备侵蚀问题得到有效解决。Sixth: After treatment, phosphogypsum is used as raw material in the process of phosphogypsum acid production and co-production of cement. Due to the reduction of fluorine content, the content of fluoride in the drying flue gas is relatively reduced, and the problem of equipment erosion is effectively solved.
其七:采用的不同浓度柠檬酸加水洗处理后的磷石膏化学组成含量(m%),5%和0.5%柠檬酸水溶液配合水洗效果最佳(3#样品中P2O5、F-质量分数最小),如表2所示。Seventh: The chemical composition content (m%) of phosphogypsum after washing with different concentrations of citric acid and water, the effect of 5% and 0.5% citric acid aqueous solution combined with water washing is the best (P 2 O 5 , F -mass in 3# sample score is the smallest), as shown in Table 2.
表2不同浓度柠檬酸加水洗处理后的磷石膏化学组成含量(m%)*
*:采用X射线荧光分析仪对净化后样品进行化学成分分析。*: X-ray fluorescence analyzer was used to analyze the chemical composition of the purified sample.
附图说明Description of drawings
图1是本发明采用的柠檬酸加水洗处理前(A)和处理后(B)的磷石膏XRD图谱。Fig. 1 is the XRD pattern of phosphogypsum before (A) and after (B) treatment of citric acid plus water washing used in the present invention.
图2是本发明所采用的柠檬酸加水洗处理前磷石膏的SEM图。Fig. 2 is the SEM image of the phosphogypsum before the citric acid plus water washing treatment used in the present invention.
图3是本发明所采用的柠檬酸加水洗处理后磷石膏在不同的放大倍数下SEM图。Fig. 3 is an SEM image of phosphogypsum at different magnifications after washing with citric acid and water used in the present invention.
根据附图进一步解释具体实施方式Further explain the specific embodiment according to the accompanying drawings
图1是本发明采用的柠檬酸加水洗处理前(A)和处理后(B)的磷石膏XRD图谱,插图表示的是磷石膏在X射线下所表现出的图谱特点。本发明根据对不同浓度柠檬酸加水洗处理磷石膏比较,选择质量浓度为5%的柠檬酸溶解和质量浓度为0.5%的柠檬酸洗涤与水洗相结合的方法,图A为处理前磷石膏原料XRD图,根据Jade软件,磷石膏主要成分是CaSO4·2H2O和SiO2,其PDF卡片编号分别为33-0311、44-0696,同时本底有大小不一的漫散峰,其中含有少量的P2O5,其PDF卡片编号为23-1301。图B为处理后磷石膏原料XRD图,根据Jade软件分析,主要成分CaSO4·2H2O没有发生改变,但净化后的样品内含有少量的CaPO3(OH)·2H2O。Fig. 1 is the XRD spectrum of phosphogypsum before (A) and after (B) treatment of the citric acid plus water washing treatment adopted in the present invention, and the illustration shows the spectrum characteristics of phosphogypsum under X-ray. According to the comparison of phosphogypsum treated with water washing with different concentrations of citric acid, the method of combining citric acid dissolution with a mass concentration of 5% and washing with citric acid with a mass concentration of 0.5% is selected. Figure A is the raw material of phosphogypsum before treatment. According to the XRD diagram, according to the Jade software, the main components of phosphogypsum are CaSO 4 2H 2 O and SiO 2 , and their PDF card numbers are 33-0311 and 44-0696 respectively. At the same time, there are diffuse peaks of different sizes in the background, which contain A small amount of P 2 O 5 has a PDF card number 23-1301. Figure B is the XRD pattern of the treated phosphogypsum raw material. According to Jade software analysis, the main component CaSO 4 ·2H 2 O has not changed, but the purified sample contains a small amount of CaPO 3 (OH) · 2H 2 O.
图2是本发明所采用的柠檬酸加水洗处理前磷石膏的SEM图,表示处理前磷石膏晶体所表现出的形状和杂质情况。图中显示磷石膏颗粒呈规则的平行四边形板块状,单个颗粒表面密实附着有大量的细小杂质颗粒。根据扫描电子显微镜图看出,磷石膏主要呈灰色,磷石膏整体呈现比较规则的平行四边形的板状结构,大部分的晶形较为规则,且表面附着有大量颗粒杂质,是可溶性磷、氟和有机质等。Fig. 2 is the SEM image of the phosphogypsum used in the present invention before washing with citric acid and water, showing the shape and impurities of the phosphogypsum crystals before treatment. The figure shows that the phosphogypsum particles are in the shape of a regular parallelogram plate, and a large number of fine impurity particles are densely attached to the surface of a single particle. According to the scanning electron microscope image, it can be seen that phosphogypsum is mainly gray in color, and the overall phosphogypsum presents a relatively regular parallelogram plate structure. Wait.
图3是本发明所采用的柠檬酸加水洗处理后磷石膏在不同的放大倍数下SEM图,图A是磷石膏原料在经过柠檬酸水溶液溶解,并经稀释后柠檬酸水溶液洗涤,最后经过两次水洗后得到的磷石膏样品在450倍放大倍数下,和净化前磷石膏样品相比,杂质得到明显去除,整体干净,磷石膏整体呈平行四边形结构。图B是磷石膏原料在经过柠檬酸水溶液溶解,并经稀释后柠檬酸水溶液洗涤,最后经过两次水洗后得到的磷石膏样品在2200倍放大倍数下看磷石膏晶须图,杂质去除干净,晶须层次分明,轮廓清晰,说明净化后的磷石膏去除了一定的Ca(H2PO4)2、CaHPO4、Ca3(PO4)2和有机物等杂质。Fig. 3 is the SEM figure of phosphogypsum under different magnifications after the citric acid and water washing treatment adopted in the present invention, Fig. A is that the raw material of phosphogypsum is dissolved in citric acid aqueous solution, and washed with citric acid aqueous solution after dilution, and finally passes through two Compared with the phosphogypsum sample before purification, the impurities of the phosphogypsum sample obtained after the first water washing are obviously removed at a magnification of 450 times, and the whole is clean, and the phosphogypsum has a parallelogram structure as a whole. Figure B is the phosphogypsum raw material dissolved in citric acid aqueous solution, washed with citric acid aqueous solution after dilution, and finally washed twice with water. The phosphogypsum whisker diagram is viewed at a magnification of 2200 times, and the impurities are removed. The whiskers have distinct layers and clear outlines, indicating that the purified phosphogypsum has removed certain impurities such as Ca(H 2 PO 4 ) 2 , CaHPO 4 , Ca 3 (PO 4 ) 2 and organic matter.
具体实施方式:一种用于去除磷石膏中杂质氟的柠檬酸加水洗的工艺方法,包括柠檬酸溶解、柠檬酸洗涤和水洗三道工序。其特征在于:所述柠檬酸溶液可与磷石膏中杂质发生化学作用,使磷石膏中氟化物和磷酸盐等杂质转化成可水洗的易溶性物质,再通过水洗工艺进行除杂,使净化后的磷石膏能更好的被磷石膏制酸联产水泥工艺利用,从而降低烘干烟气中的氟化物含量,同时不影响硫酸和水泥生产工艺,本发明的制备过程包括如下步骤:Specific embodiments: a process method of citric acid plus water washing for removing impurity fluorine in phosphogypsum, including three processes of citric acid dissolution, citric acid washing and water washing. It is characterized in that: the citric acid solution can chemically react with impurities in phosphogypsum, so that impurities such as fluoride and phosphate in phosphogypsum can be converted into water-washable and easily soluble substances, and then impurities can be removed by water washing process, so that after purification The phosphogypsum can be better utilized by the phosphogypsum acid co-production cement process, thereby reducing the fluoride content in the drying flue gas without affecting the sulfuric acid and cement production process. The preparation process of the present invention includes the following steps:
第一步是配制不同浓度柠檬酸溶液:用精度为百分之一的电子天平分别准确称取柠檬酸3.00g、4.00g、5.00g、6.00g和7.00g,分别配比质量浓度为3%、4%、5%、6%和7%的柠檬酸水溶液备用,再从上述配制好的柠檬酸水溶液中分别量取10mL置于150mL烧杯中,各加入90mL去离子水,将其稀释为质量浓度为0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液备用;The first step is to prepare different concentrations of citric acid solutions: accurately weigh 3.00g, 4.00g, 5.00g, 6.00g and 7.00g of citric acid with an electronic balance with an accuracy of 1%, respectively, and the proportioning mass concentration is 3%. , 4%, 5%, 6% and 7% citric acid aqueous solutions for later use, then measure 10mL from the above prepared citric acid aqueous solution and place them in 150mL beakers, add 90mL deionized water each, and dilute it to mass Concentration is the citric acid aqueous solution of 0.3%, 0.4%, 0.5%, 0.6% and 0.7% standby;
第二步是用柠檬酸加水洗处理磷石膏:用精度为百分之一的电子天平称取9.00g~9.60g的磷石膏原料样品六份,分别置于相同刻度与大小的玻璃器皿中,再分别取10mL的3%、4%、5%、6%和7%的柠檬酸水溶液加入到磷石膏样品中,机械搅拌15~25min直至溶解,溶解后的混合物经过过滤装置过滤,滤液移至收集槽收集,用质量浓度0.3%、0.4%、0.5%、0.6%和0.7%的柠檬酸水溶液对过滤后的滤渣进行超声分散洗涤6~10min,并在离心机中以3000~4000rpm转速离心8~12min,然后加入纯水超声分散洗涤并旋转离心2次,离心后得到的净化后磷石膏样品1#、2#、3#、4#、5#,再将净化后的磷石膏样品经过85℃的电热恒温鼓风干燥箱内干燥12h,得到成品;The second step is to wash the phosphogypsum with citric acid and water: use an electronic balance with an accuracy of 1% to weigh six samples of phosphogypsum raw materials of 9.00g~9.60g, and place them in glassware with the same scale and size. Then take 10mL of 3%, 4%, 5%, 6% and 7% citric acid aqueous solution into the phosphogypsum sample, stir mechanically for 15~25min until dissolved, the dissolved mixture is filtered through the filter device, and the filtrate is transferred to Collect in the collection tank, use citric acid aqueous solution with mass concentration of 0.3%, 0.4%, 0.5%, 0.6% and 0.7% to ultrasonically disperse and wash the filtered filter residue for 6~10min, and centrifuge at 3000~4000rpm in a centrifuge for 8 ~12min, then add pure water for ultrasonic dispersion washing and spin centrifugation twice, the purified phosphogypsum samples 1 # , 2 # , 3 # , 4 # , 5 # after centrifugation, and then pass the purified phosphogypsum samples through 85 ℃ for 12 hours in an electric heating constant temperature blast drying oven to obtain the finished product;
第三步是石灰中和处理水洗废水:配比质量浓度为0.3~0.5%的石灰水加入到废液收集槽中,搅拌8~12min,得到均匀料浆,用pH计测定料浆的pH值,并加入质量浓度为85~95%的石灰水将此料浆的pH值调节至7;最后加入明矾溶液,在废水处理槽内搅拌10~15min后静置分层,得到上层pH值为7的中和水和下层难溶的沉淀物。The third step is lime neutralization to treat washing wastewater: add lime water with a mass concentration of 0.3-0.5% into the waste liquid collection tank, stir for 8-12 minutes to obtain a uniform slurry, and measure the pH value of the slurry with a pH meter , and add lime water with a mass concentration of 85-95% to adjust the pH value of the slurry to 7; finally add alum solution, stir in the wastewater treatment tank for 10-15 minutes, and then let it stand for stratification to obtain a pH value of 7 in the upper layer. The neutralized water and the insoluble sediment in the lower layer.
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