TW200925112A - Method of recovering rare earth elements - Google Patents
Method of recovering rare earth elements Download PDFInfo
- Publication number
- TW200925112A TW200925112A TW97137448A TW97137448A TW200925112A TW 200925112 A TW200925112 A TW 200925112A TW 97137448 A TW97137448 A TW 97137448A TW 97137448 A TW97137448 A TW 97137448A TW 200925112 A TW200925112 A TW 200925112A
- Authority
- TW
- Taiwan
- Prior art keywords
- rare earth
- recovered
- carbonate
- solution
- ammonium
- Prior art date
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- 229910052761 rare earth metal Inorganic materials 0.000 title claims abstract description 165
- 238000000034 method Methods 0.000 title claims abstract description 71
- -1 sulfuric acid compound Chemical class 0.000 claims abstract description 116
- 239000002002 slurry Substances 0.000 claims abstract description 68
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 52
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 49
- QAOWNCQODCNURD-UHFFFAOYSA-N sulfuric acid Substances OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 46
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims abstract description 44
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims abstract description 44
- 235000011130 ammonium sulphate Nutrition 0.000 claims abstract description 43
- 239000002699 waste material Substances 0.000 claims abstract description 43
- 229910001404 rare earth metal oxide Inorganic materials 0.000 claims abstract description 32
- 238000001354 calcination Methods 0.000 claims abstract description 27
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims abstract description 22
- 238000000227 grinding Methods 0.000 claims abstract description 19
- 150000003863 ammonium salts Chemical class 0.000 claims abstract description 8
- 238000002156 mixing Methods 0.000 claims abstract description 7
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims description 43
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 claims description 41
- 235000012538 ammonium bicarbonate Nutrition 0.000 claims description 41
- 239000001099 ammonium carbonate Substances 0.000 claims description 41
- 239000007864 aqueous solution Substances 0.000 claims description 36
- 239000007788 liquid Substances 0.000 claims description 34
- 239000000243 solution Substances 0.000 claims description 34
- 239000007789 gas Substances 0.000 claims description 33
- 238000000926 separation method Methods 0.000 claims description 33
- 150000002910 rare earth metals Chemical class 0.000 claims description 29
- 239000003795 chemical substances by application Substances 0.000 claims description 28
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 19
- 239000007787 solid Substances 0.000 claims description 18
- 238000010438 heat treatment Methods 0.000 claims description 15
- 238000002425 crystallisation Methods 0.000 claims description 14
- 230000008025 crystallization Effects 0.000 claims description 14
- 238000001914 filtration Methods 0.000 claims description 13
- 239000000463 material Substances 0.000 claims description 11
- 239000003002 pH adjusting agent Substances 0.000 claims description 11
- 230000001376 precipitating effect Effects 0.000 claims description 11
- 239000002994 raw material Substances 0.000 claims description 11
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims description 9
- 229910052731 fluorine Inorganic materials 0.000 claims description 9
- 239000011737 fluorine Substances 0.000 claims description 9
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 claims description 7
- 239000002253 acid Substances 0.000 claims description 7
- 238000010979 pH adjustment Methods 0.000 claims description 7
- 238000004064 recycling Methods 0.000 claims description 6
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims description 5
- 229910052784 alkaline earth metal Inorganic materials 0.000 claims description 5
- 238000001704 evaporation Methods 0.000 claims description 5
- 230000008020 evaporation Effects 0.000 claims description 5
- 239000002689 soil Substances 0.000 claims description 5
- 229910052783 alkali metal Inorganic materials 0.000 claims description 4
- 238000004821 distillation Methods 0.000 claims description 4
- 239000002904 solvent Substances 0.000 claims description 4
- 229910021653 sulphate ion Inorganic materials 0.000 claims description 4
- 150000001340 alkali metals Chemical class 0.000 claims description 3
- 239000012298 atmosphere Substances 0.000 claims description 3
- BVKZGUZCCUSVTD-UHFFFAOYSA-N carbonic acid Chemical compound OC(O)=O BVKZGUZCCUSVTD-UHFFFAOYSA-N 0.000 claims description 3
- 150000001875 compounds Chemical class 0.000 claims description 3
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 2
- 229910000288 alkali metal carbonate Inorganic materials 0.000 claims description 2
- 150000008041 alkali metal carbonates Chemical class 0.000 claims description 2
- 239000000376 reactant Substances 0.000 claims description 2
- 229910052717 sulfur Inorganic materials 0.000 claims description 2
- 239000011593 sulfur Substances 0.000 claims description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims 2
- 229910052799 carbon Inorganic materials 0.000 claims 2
- WWILHZQYNPQALT-UHFFFAOYSA-N 2-methyl-2-morpholin-4-ylpropanal Chemical compound O=CC(C)(C)N1CCOCC1 WWILHZQYNPQALT-UHFFFAOYSA-N 0.000 claims 1
- 239000005084 Strontium aluminate Substances 0.000 claims 1
- RQPZNWPYLFFXCP-UHFFFAOYSA-L barium dihydroxide Chemical compound [OH-].[OH-].[Ba+2] RQPZNWPYLFFXCP-UHFFFAOYSA-L 0.000 claims 1
- 229910001863 barium hydroxide Inorganic materials 0.000 claims 1
- 239000013590 bulk material Substances 0.000 claims 1
- 238000004181 pedogenesis Methods 0.000 claims 1
- 238000007670 refining Methods 0.000 claims 1
- FNWBQFMGIFLWII-UHFFFAOYSA-N strontium aluminate Chemical compound [O-2].[O-2].[O-2].[O-2].[O-2].[Al+3].[Al+3].[Sr+2].[Sr+2] FNWBQFMGIFLWII-UHFFFAOYSA-N 0.000 claims 1
- 239000000203 mixture Substances 0.000 abstract description 14
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 51
- 238000006243 chemical reaction Methods 0.000 description 47
- 238000010521 absorption reaction Methods 0.000 description 32
- 235000011089 carbon dioxide Nutrition 0.000 description 25
- 238000011084 recovery Methods 0.000 description 20
- 238000005498 polishing Methods 0.000 description 19
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 18
- 229910021529 ammonia Inorganic materials 0.000 description 15
- 239000001569 carbon dioxide Substances 0.000 description 13
- 229910002092 carbon dioxide Inorganic materials 0.000 description 13
- 230000002378 acidificating effect Effects 0.000 description 12
- 238000001035 drying Methods 0.000 description 12
- 238000003756 stirring Methods 0.000 description 11
- 239000000047 product Substances 0.000 description 10
- 229910052742 iron Inorganic materials 0.000 description 9
- 230000015572 biosynthetic process Effects 0.000 description 8
- 239000011521 glass Substances 0.000 description 8
- 239000012535 impurity Substances 0.000 description 8
- 239000000706 filtrate Substances 0.000 description 7
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 6
- 238000005755 formation reaction Methods 0.000 description 6
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 5
- 229910052751 metal Inorganic materials 0.000 description 5
- 239000002184 metal Substances 0.000 description 5
- DDFHBQSCUXNBSA-UHFFFAOYSA-N 5-(5-carboxythiophen-2-yl)thiophene-2-carboxylic acid Chemical compound S1C(C(=O)O)=CC=C1C1=CC=C(C(O)=O)S1 DDFHBQSCUXNBSA-UHFFFAOYSA-N 0.000 description 4
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 4
- 239000003082 abrasive agent Substances 0.000 description 4
- 239000003929 acidic solution Substances 0.000 description 4
- 239000003513 alkali Substances 0.000 description 4
- 238000004458 analytical method Methods 0.000 description 4
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 4
- 229910000420 cerium oxide Inorganic materials 0.000 description 4
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 description 4
- 238000010992 reflux Methods 0.000 description 4
- 150000003839 salts Chemical class 0.000 description 4
- 238000004062 sedimentation Methods 0.000 description 4
- 229910052782 aluminium Inorganic materials 0.000 description 3
- WUKWITHWXAAZEY-UHFFFAOYSA-L calcium difluoride Chemical compound [F-].[F-].[Ca+2] WUKWITHWXAAZEY-UHFFFAOYSA-L 0.000 description 3
- 229910001634 calcium fluoride Inorganic materials 0.000 description 3
- 239000003153 chemical reaction reagent Substances 0.000 description 3
- 238000004090 dissolution Methods 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 239000005337 ground glass Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical group [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 3
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 3
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 239000000758 substrate Substances 0.000 description 3
- 238000003786 synthesis reaction Methods 0.000 description 3
- 241000255925 Diptera Species 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- PIFAXYQNMFVFQX-UHFFFAOYSA-N [N].OC(O)=O Chemical compound [N].OC(O)=O PIFAXYQNMFVFQX-UHFFFAOYSA-N 0.000 description 2
- 238000013019 agitation Methods 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- AYJRCSIUFZENHW-UHFFFAOYSA-L barium carbonate Chemical compound [Ba+2].[O-]C([O-])=O AYJRCSIUFZENHW-UHFFFAOYSA-L 0.000 description 2
- TZCXTZWJZNENPQ-UHFFFAOYSA-L barium sulfate Chemical compound [Ba+2].[O-]S([O-])(=O)=O TZCXTZWJZNENPQ-UHFFFAOYSA-L 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 2
- 239000000920 calcium hydroxide Substances 0.000 description 2
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 2
- 239000001175 calcium sulphate Substances 0.000 description 2
- 235000011132 calcium sulphate Nutrition 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-M hydrogensulfate Chemical compound OS([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-M 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 238000011027 product recovery Methods 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- 239000007858 starting material Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000001117 sulphuric acid Substances 0.000 description 2
- 235000011149 sulphuric acid Nutrition 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- KJTLSVCANCCWHF-UHFFFAOYSA-N Ruthenium Chemical compound [Ru] KJTLSVCANCCWHF-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- RGMIJWDPTWPGJV-UHFFFAOYSA-N [NH4+].[Ar].C([O-])([O-])=O.[NH4+] Chemical compound [NH4+].[Ar].C([O-])([O-])=O.[NH4+] RGMIJWDPTWPGJV-UHFFFAOYSA-N 0.000 description 1
- NJFMNPFATSYWHB-UHFFFAOYSA-N ac1l9hgr Chemical compound [Fe].[Fe] NJFMNPFATSYWHB-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 238000010306 acid treatment Methods 0.000 description 1
- 230000004520 agglutination Effects 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- 239000000908 ammonium hydroxide Substances 0.000 description 1
- 229910001570 bauxite Inorganic materials 0.000 description 1
- 210000004556 brain Anatomy 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 229910052792 caesium Inorganic materials 0.000 description 1
- TVFDJXOCXUVLDH-UHFFFAOYSA-N caesium atom Chemical compound [Cs] TVFDJXOCXUVLDH-UHFFFAOYSA-N 0.000 description 1
- 159000000007 calcium salts Chemical class 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 125000005626 carbonium group Chemical group 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 1
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 description 1
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 210000003298 dental enamel Anatomy 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- MAHNFPMIPQKPPI-UHFFFAOYSA-N disulfur Chemical compound S=S MAHNFPMIPQKPPI-UHFFFAOYSA-N 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 238000004993 emission spectroscopy Methods 0.000 description 1
- 239000012065 filter cake Substances 0.000 description 1
- 238000003682 fluorination reaction Methods 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 125000004435 hydrogen atom Chemical group [H]* 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 150000002506 iron compounds Chemical class 0.000 description 1
- 239000004973 liquid crystal related substance Substances 0.000 description 1
- 238000004020 luminiscence type Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000008267 milk Substances 0.000 description 1
- 210000004080 milk Anatomy 0.000 description 1
- 235000013336 milk Nutrition 0.000 description 1
- 239000011268 mixed slurry Substances 0.000 description 1
- 239000010812 mixed waste Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- JRZJOMJEPLMPRA-UHFFFAOYSA-N olefin Natural products CCCCCCCC=C JRZJOMJEPLMPRA-UHFFFAOYSA-N 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 229910052762 osmium Inorganic materials 0.000 description 1
- SYQBFIAQOQZEGI-UHFFFAOYSA-N osmium atom Chemical compound [Os] SYQBFIAQOQZEGI-UHFFFAOYSA-N 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000007517 polishing process Methods 0.000 description 1
- 229920000515 polycarbonate Polymers 0.000 description 1
- 239000004417 polycarbonate Substances 0.000 description 1
- 238000006116 polymerization reaction Methods 0.000 description 1
- 239000012495 reaction gas Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 229910052707 ruthenium Inorganic materials 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 1
- 238000001694 spray drying Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000001291 vacuum drying Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004876 x-ray fluorescence Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B59/00—Obtaining rare earth metals
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/02—Roasting processes
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/006—Wet processes
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Geology (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Geochemistry & Mineralogy (AREA)
- Grinding-Machine Dressing And Accessory Apparatuses (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
Description
200925112 六、發明說明: 【發明所屬之技術領域】 本發明係關於自含有稀土類元素之漿料回收稀土類氧化 物之方法,尤其是關於自廢研磨漿料回收可再利用作為高精 度研磨加工用之原料的高品質稀土類氧化物的廉價製程。 【先前技術】 -以鈽、鑭為主成分之稀土類系研磨劑(以下有時簡稱為「研 ❹ 磨劑」),被廣泛使用作為硬碟等之磁性記錄媒體用玻璃基 板、光學透鏡、液晶顯示器之玻璃基板、光罩用玻璃基板等 各種玻璃材料研磨用之研磨劑。 在以上述研磨劑進行各種玻璃材料之研磨時,係作成使經 微粒化之該述研磨劑分散於水系分散劑中之研磨劑漿料,使 該漿料於被研磨材之玻璃材料與研磨墊之間流動,藉此進行 研磨作業。 ❹ 通常,研磨劑漿料係於研磨製程中回收使用。經回收時, 將因所研磨之玻璃成分之累積而使研磨特性逐漸降低,故藉 由斷續地置換新鮮的研磨賴料以達到維持研磨效率。 自研磨製程所取出之廢研磨舰 化鐵、高分子凝集綱使其沉降' ^化銘或氯 與產業廢棄觸等之處置進行虛 /ιν"77離後之濕滤餅以 了_外,尚多量地含有網、該廢棄物中,除200925112 VI. Description of the Invention: [Technical Field] The present invention relates to a method for recovering rare earth oxides from a slurry containing rare earth elements, and more particularly relates to recycling of waste abrasive slurry for reuse as a high precision grinding process An inexpensive process for producing high quality rare earth oxides from raw materials. [Prior Art] A rare earth-based abrasive containing ruthenium and osmium as a main component (hereinafter sometimes referred to as "sludge abrasive") is widely used as a glass substrate for magnetic recording media such as a hard disk, an optical lens, and the like. An abrasive for polishing various glass materials such as a glass substrate of a liquid crystal display or a glass substrate for a photomask. When polishing various glass materials with the above-mentioned polishing agent, the polishing slurry is prepared by dispersing the atomized abrasive in the aqueous dispersion, and the slurry is applied to the glass material of the material to be polished and the polishing pad. Flow between them to perform the grinding operation. ❹ Generally, the abrasive slurry is recycled for use in the polishing process. Upon recovery, the polishing characteristics are gradually lowered due to the accumulation of the ground glass components, so that the polishing efficiency is maintained by intermittently replacing the fresh abrasive materials. The waste grinding of the wrecked iron and the polymer agglutination unit taken out from the grinding process to make it settled ^ ^ Hua Ming or chlorine and the disposal of industrial waste, such as the virtual / ιν " 77 after the wet cake was _ outside, still a large amount of nets, the waste, except
Earth Elements,稀土類元素)、等之貝重稀土族(Rare 此’不將此等單純地予 097137448 200925112Earth Elements, rare earth elements), etc. Residual rare earths (Rare this does not simply give this to 097137448 200925112
具意義。因此, w力切’而進行回收再使用一事,係由稀土 -穩疋確保或資源之有效利用的觀點而言極 期盼自使用完畢之廢研磨劑漿料回收稀土類 成分並再利用的低成本回收_。 作為將使用完畢之研磨_收的方法, 習知已知有例如日 本專利第3615943號公報(專利文獻〇、曰本專利公開公報 (特開2004-175652號)(專利文獻2)、日本專利公開公報(特 ❹開2003-211356號)(專利文獻3)所記載般進行酸處理,以 回收成為研磨劑原料之稀土類元素的方法,或如曰本專利第 3134189號公報(專利文獻4)、日本專利公開公報(特開 2003-205460號)(專利文獻5)記載般進行鹼處理,以再生作 為研磨劑之方法。 然而,習知之任一種方法均有問題。亦即,(丨)雖可回收 稀土類元素,但將產生含有氨之大量廢水或副產生廢棄物, ❹以及(ii)難以使溶存於所回收之稀土類元素中的鐵成分或 鋁成分完全分離等品質方面的問題。 尤其是將廢研磨劑溶解於酸而進行回收時,若使用碳酸氫 錄作為中和劑,則可依過濾性良好之碳酸稀土的型式進行回 收,而屬較佳。但該方法中,將有使用高價之碳酸氫銨、或 副產生含有高濃度之氨的廢液而因其之無害化處理等,耗費 大幅成本的問題。 本發明之目的在於提供一種解決上述習知方法的問題 097137448 4 200925112 點’自含有稀土類元素之廢研磨劑聚料效率良好地回收高品 質之稀土類氧化物的廉價製程。 本發明者等人為了達成此種目的而潛心研究,結果發現, ⑴於使用碳酸氫銨作為中和劑的方法中自從反應所副產 生之碳酸氣體與㈣水雜分離⑽與NH3,將其回收使用 ,作為破酸氫録,同時,另外(ii)在分離、回收碳酸稀土類(以 .下有時稱為「碳酸稀土」)時,預先以特定之pH進行固液分 ❹離,藉此可選擇性地使溶解共存之鐵離子等之雜質沉殿去 除,而可輕易地製造高純度之碳酸稀土類,遂完成本發明。 另外’又發現於上述方法中’藉由在含有氧化稀土之廢研 磨劑漿料中添加硫麟,則可使氧化稀土成為可溶性之硫酸 稀土 ’以及藉由回收產生為廢液之硫酸銨溶液,回收至上述 反應用’則可構成幾乎不產生副產物之稀土類元素回收製 程,而根據此等見解,完成了本發明。 G 【發明内容】 依照本發明,提供以下之伴隨有硫酸銨(Ammonium Sul fate)之再利用的稀土類元素之回收方法。 [1] 一種稀土類元素之回收方法,其特徵為,在包括下述步驟 (1M5)之第一步驟[I]申,自含有稀土類元素之氧化物的廢 研磨劑漿料回收該稀土類氧化物,其次於包括下述步驟(6) 之第二步驟[II]中,回收第1步驟[I]所使用之硫酸敍,將 097137448 5 200925112 該回收硫酸銨於上述第一步驟[i]中進行再利用。 於此’第一步驟[I]係包括: (1) 將含有稀土類氧化物(Rare Earth Oxide)之漿料與硫 酸化合物混合,進行加熱焙燒作成硫酸豨土(Rare Earth Sulfate),將其溶解於水(步驟; (2) 將所得之硫酸稀土溶液之pH調節為適當條件後,藉固 液分離手段分離不溶解成分(步驟(2)); ❹ (3)於該硫酸稀土溶液中添加沉殿劑而使碳酸稀土( RareMeaningful. Therefore, it is highly desirable to recover rare earth components from the used waste abrasive slurry and reuse it from the viewpoint of ensuring the recovery of rare earths - stable or efficient use of resources. Cost recovery _. For example, Japanese Patent No. 3,615,943 (Patent Document No. JP-A-2004-175652) (Patent Document 2), Japanese Patent Publication No. (Japanese Patent No. 2003-211356) (Patent Document 3), a method of performing an acid treatment to recover a rare earth element which is a raw material of an abrasive, or a method of Japanese Patent No. 3134189 (Patent Document 4), Japan In the patent publication (Japanese Laid-Open Patent Publication No. 2003-205460) (Patent Document 5), a method of performing alkali treatment to regenerate an abrasive is described. However, any of the conventional methods has problems. That is, (丨) can be recycled. A rare earth element, however, causes a large amount of wastewater containing ammonia or by-produced waste, and (ii) a problem that it is difficult to completely separate the iron component or the aluminum component dissolved in the recovered rare earth element. When the waste abrasive is dissolved in an acid and recovered, if hydrogen carbonate is used as a neutralizing agent, it can be recovered according to the type of rare earth carbonate having good filterability. However, in this method, there is a problem in that a high-priced ammonium hydrogencarbonate or a waste liquid containing a high concentration of ammonia is used to cause a wasteful treatment, which is costly, etc., and the like. Problems of the conventional method 097137448 4 200925112 Point 'Inexpensive process for efficiently recovering high-quality rare earth oxides from waste abrasive aggregates containing rare earth elements. The present inventors have diligently studied to achieve such a purpose. As a result, it was found that (1) in the method using ammonium hydrogencarbonate as a neutralizing agent, since the carbonic acid gas generated by the reaction is separated from (4) water, (10) and NH3, it is recycled and used as a hydrogen peroxide, and (ii) When separating and recovering rare earth carbonates (sometimes referred to as "rare earth carbonates"), the solid-liquid separation is carried out at a specific pH in advance, whereby the impurities such as iron ions dissolved in the coexistence can be selectively precipitated. The temple is removed, and high-purity rare earth carbonates can be easily produced, and the present invention is completed. In addition, 'it was found in the above method' by using waste grinding in the rare earth containing rare earth When sulfur sulphide is added to the slurry, the oxidized rare earth can be made into a soluble rare earth sulphate and the ammonium sulphate solution which is produced as a waste liquid can be recovered, and the above-mentioned reaction can be recovered to constitute a rare earth element recovery which hardly produces by-products. According to the present invention, the present invention has been completed. According to the present invention, the following method for recovering rare earth elements accompanied by reuse of ammonium sulfate (Ammonium Sulfate) is provided. [1] A rare earth A method for recovering a class of elements, characterized in that, in a first step [I] comprising the following step (1M5), the rare earth oxide is recovered from a waste abrasive slurry containing an oxide of a rare earth element, secondarily In the second step [II] including the following step (6), the sulfuric acid used in the first step [I] is recovered, and the recovered ammonium sulfate in 097137448 5 200925112 is reused in the first step [i]. Here, the first step [I] includes: (1) mixing a slurry containing a rare earth oxide (Rare Earth Oxide) with a sulfuric acid compound, heating and roasting to form a barium sulfate (Rare Earth Sulfate), and dissolving it. In water (step; (2) after adjusting the pH of the obtained rare earth sulfate solution to an appropriate condition, separating the insoluble component by solid-liquid separation means (step (2)); ❹ (3) adding a sink to the rare earth sulfate solution Rare earth carbonate (Rare
Earth Carbonate)進行晶析(步驟(3)); (4)自所得之含有碳酸稀土之漿料使碳酸稀土分離(步驟 (4));以及 (5)將其進行煅燒作成稀土類氧化物,回收所生成之稀土 類元素(步驟(5)); 另外,第二步驟[II]係包括: ❹ (6)在步驟(2)之pH調節劑及步驟(3)之沉澱劑含有氨水 或含銨鹽時,將分離了碳酸稀土之硫酸銨水溶液進行遭端, 分離回收高濃度之硫酸銨水溶液,將回收之硫酸銨水溶液再 利用作為使硫酸稀土形成的反應劑(步驟(6))。 [2] 如[1]記載之方法’係於第一步驟Π]與硫酸銨一起回收& 並於該第一步驟[I]中再利用者,將經分離了碳酸稀土〜 酸銨水溶液進行濃縮,將高濃度之硫酸銨水溶液與水八 097137448 6 200925112 離回收,經 [3] 回收之水係再 利用為使硫酸稀土溶解之溶媒。 如[1]或[2]記載之大 (7).(8)^^^ 方法,係進一步實施含有其次之步驟 「11夕—^步驟[111]者,將[1]或[2]所記載之第一步驟 [1]之步驟(3)中估用从* 文用作為使碳酸稀土形成之沉澱劑的碳酸 氫銨回收,於卜、+,丰 、上述步驟(3)中再利用。 於此,第三步驟[III]係包括: ❹ ❹ ()、將加熱培燒步驟所產生之IlIL及氨氣回收至水溶液 中於其添加沉澱劑使氟成分沉澱,將其藉過濾去除,藉此 回收氨水溶液(步驟(7));與 (8)接著對所回收之氨水溶液,使於pH調整步驟、碳酸稀 土晶析步驟及煅燒步驟所產生之碳酸氣體接觸而形成碳酸 氮按之溶液或漿料,將所得之碳酸氫銨之溶液或漿料再利用 於晶析步驟中作為使碳酸稀土形成的沉澱劑(步驟(8))。 [4] 如[丨]或[2]記载之方法,其中,步驟(1)之硫酸化合物為 硫酸銨或硫酸氫錢。 [5] 如[丨]或[2]記載之方法’其中,步驟(丨)之焙燒溫度為300 °C以上。 [6] 如[丨]或[2]記載之方法’其中,步驟(2)之PH條件為4-7, 097137448 7 200925112 pH調節劑為可溶性之鹼金屬鹽、銨鹽或氨水。 [7] 如[1]或[2]記載之方法,其中,步驟(2)中之不溶解成分 之固液分離手段係藉過濾所進行。 [8] -如[1]或[2]記載之方法,其中,步驟(3)之沉澱劑為銨鹽、 驗金屬之碳酸鹽、驗土類金屬之碳酸鹽、驗金屬之碳酸氫鹽 Q 或鹼土類金屬之碳酸氫鹽中之至少一種以上。 [9] 如[1]或[2]記載之方法,其中,步驟(3)之沉澱劑為碳酸 氫銨。 [10] 如[1]、[2]或[8]記載之方法,於步驟[3]所添加之沉澱劑 的形態為固體、溶液或漿料狀。 Ο [11] 如[1]或[2]記載之方法,其中,於步驟(4)中,將所生成 之碳酸稀土進行過濾、洗淨並分離、精製。 [12] 如[1]或[2]記載之方法,其中,於步驟(5)之煅燒係於空 氣環境中且溫度為300-1200°C。 [13] 如[1]或[2]記載之方法,其中,步驟(6)之濃縮分離為蒸 097137448 200925112 餾或蒸發。 [14] 如[1]或[2]記載之方法,其中,步驟(7)之沉澱劑為氫氧 化I弓。 [15] -如[1]或[2]記載之方法,其中,步驟(8)中,接觸溫度為 10-40。。。 〇 [16] 如[1]或[2]記載之方法,其中,步驟(8)中之碳酸氫銨之 濃度為5-25質量%,其形態為溶液或漿料。 [17] 一種稀土類元素之回收方法,係將研磨劑使用於研磨,自 所產生之廢研磨劑漿料藉[1]-[16]之任一項記載之方法回 收稀土類元素,將所得之稀土類元素再次使用作為研磨劑原 〇 料。 【實施方式】 以下,參照圖式詳細說明本發明。圖1為顯示本發明特徵 之包括碳酸氫銨之回收步驟及硫酸銨等之回收步驟的稀土 類元素之回收步驟的流程圖。於此,廢研磨劑漿料10係成 為回收處理對象之起始漿料。 (廢研磨劑漿料) 廢研磨劑漿料10中,除了主成分之氧化稀土(Rare Earth 097137448 9 200925112Earth Carbonate) is carried out (step (3)); (4) separating the rare earth carbonate from the obtained rare earth carbonate-containing slurry (step (4)); and (5) calcining it to form a rare earth oxide, Recovering the generated rare earth element (step (5)); in addition, the second step [II] includes: ❹ (6) the pH adjuster in the step (2) and the precipitating agent in the step (3) contain ammonia water or In the case of the ammonium salt, the ammonium sulfate aqueous solution in which the rare earth carbonate is separated is subjected to the end, the high-concentration ammonium sulfate aqueous solution is separated and recovered, and the recovered ammonium sulfate aqueous solution is reused as a reactant for forming the rare earth sulfate (step (6)). [2] The method described in [1] is carried out in the first step Π with ammonium sulfate and is reused in the first step [I], and the aqueous solution of the rare earth carbonate to ammonium acid is separated. The mixture is concentrated, and a high-concentration ammonium sulfate aqueous solution is recovered from water 097137448 6 200925112, and the water recovered by [3] is reused as a solvent for dissolving rare earth sulfate. If the method of [7].(8)^^^ described in [1] or [2] is further implemented, the second step (11) will be followed by [11] or [2]. In the step (3) of the first step [1] of the description, it is estimated that the ammonium hydrogencarbonate used as a precipitating agent for forming rare earth carbonate is recovered, and reused in the above step (3). Here, the third step [III] includes: ❹ ❹ (), recovering IlIL and ammonia generated by the heating and calcining step into an aqueous solution, and adding a precipitating agent to precipitate a fluorine component, and removing it by filtration, borrowing Recovering the aqueous ammonia solution (step (7)); and (8) subsequently contacting the recovered aqueous ammonia solution with the carbonic acid gas generated in the pH adjusting step, the rare earth carbonate crystallization step and the calcining step to form a solution of carbonic acid nitrogen Or a slurry, and the obtained solution or slurry of ammonium hydrogencarbonate is reused in the crystallization step as a precipitant for forming rare earth carbonate (step (8)). [4] As described in [丨] or [2] The method wherein the sulfuric acid compound of the step (1) is ammonium sulfate or hydrogen sulfate. [5] The method described in [丨] or [2] wherein the step ( The calcination temperature is 300 ° C or higher. [6] The method described in [丨] or [2], wherein the pH condition of the step (2) is 4-7, 097137448 7 200925112 pH adjuster is a soluble alkali metal [7] The method according to [1] or [2] wherein the solid-liquid separation means of the insoluble component in the step (2) is carried out by filtration. [8] - such as [ The method according to [1], wherein the precipitating agent of the step (3) is an ammonium salt, a metal carbonate, a carbonate of a soil-based metal, a metal hydrogencarbonate Q or an alkaline earth metal carbonate. [9] The method according to [1] or [2] wherein the precipitating agent of the step (3) is ammonium hydrogencarbonate. [10] such as [1], [2] or [ 8) The method of the method of the present invention, wherein the form of the precipitant added in the step [3] is a solid, a solution or a slurry. [11] The method according to [1] or [2], wherein, in the step (4) The produced rare earth carbonate is filtered, washed, separated, and purified. [12] The method according to [1] or [2] wherein the calcination in the step (5) is carried out in an air atmosphere at a temperature of 300-1200 ° C. [ [13] The method according to [1] or [2], wherein the concentration separation in the step (6) is a distillation or evaporation of the 097137448 200925112. [14] The method according to [1] or [2], wherein the step ( 7) The precipitating agent is a hydroxide I. [15] The method according to [1] or [2] wherein, in the step (8), the contact temperature is 10-40... 〇[16] as [ The method according to [1], wherein the concentration of the ammonium hydrogencarbonate in the step (8) is 5 to 25% by mass, and the form is a solution or a slurry. [17] A method for recovering a rare earth element, wherein the abrasive is used for polishing, and the rare earth element is recovered by the method described in any one of [1] to [16]. The rare earth element is reused as an abrasive raw material. [Embodiment] Hereinafter, the present invention will be described in detail with reference to the drawings. BRIEF DESCRIPTION OF THE DRAWINGS Fig. 1 is a flow chart showing the steps of recovering rare earth elements including a recovery step of ammonium hydrogencarbonate and a recovery step of ammonium sulfate or the like which is characterized by the present invention. Here, the waste abrasive slurry 10 is a starting slurry for recycling treatment. (Waste Abrasive Slurry) In the waste abrasive slurry 10, in addition to the main component of the rare earth oxide (Rare Earth 097137448 9 200925112
Oxide)、氟化豨土(Rare Earth Fluoride)之外’尚混入有 經研磨之玻璃成分的石夕或銘化合物,破碎之玻璃屑、塾纖 維、其他異物。此廢研磨劑漿料10之成分係因所使用之製 程條件而變化’但通常係依固形份濃度約5〜50%之狀態自研 磨步驟9排出。其組成係乾燥品基準之稀土類氧化物換算量 . TRE0(=(總豨土氧化物質量/總氧化物質量)χ100))為82質 .量%(其中’約25質為氣化稀土成分),碎化合物為約5 ❹ 質量%’鋁化合物或鐵化合物為約1質量%,其他並混入有玻 璃粉或墊纖維等之異物。 廢研磨劑漿料1〇係於研磨步驟9中,將一邊進行循環、 一邊重複使用之研磨劑漿料,最終藉由重力沉降法所進行之 濃縮’調製成氣化稀土D換算(T_(Total Rare Earth Oxide))計為約3〇質量%之漿料。 、: 在該濃料之以重力沉降法進行之濃縮時,可單獨以 ©該廢研磨齊J漿料進行,但併用市售之高分子凝集劑者將更有 效地進行該沉降壤縮。此成為由步驟⑴所處理之廢研磨劑 漿料的起始原料。 (第一步驟[I]) 第-步驟[I]係包括下述步驟⑴一⑸。 (步驟(1)) (將廢研磨㈣料中之稀土類元素轉’而得到稀土類溶液 097137448 200925112 首先,於反應容器中採取廢研磨劑聚料ι〇,於其添加既 定量之硫祕等之㈣化合物(以下有時稱為「硫酸銨 等」)20作為反應藥劑’並在授拌下進行混合別。其後,將 其於乾燥步驟33、培燒步驟35中,作成薄片⑴制狀之 廢研磨劑。 ❹ •作狀應容^,並無制限定,較録至少具備擾摔手 段’廢研磨劑聚料、硫酸銨等之導入手段的養槽型者。 硫酸錄等之硫酸化合物之添加量,係相對於廢研磨劑聚料 刚份(P㈣,為40、60份、較佳為5〇份左右。若添加量 未滿40份’則稀土類元素之不溶解份變多,又,若添 超過6〇份’則無法發揮其以上之效果,僅止於使所浪費之 藥劑量增多,故不佳。又,作為硫酸化合物,除了硫酸 外,亦可使用硫酸氫錢。 ❹ 經混合之漿料可I[接移行至域步驟35,但若考慮到一 溫加熱時之裝置脑等,則較佳係預先進行乾燥抑以= 水分。 矛、 作為乾燥設備並無特別限定,可應用箱形乾燥器、帶 燥器、真空乾燥H等任意者Hi度較佳為⑼_25代^ 特佳為90-20(TC。若乾燥溫度低於_,則由乾燥效率方 面而言並不佳,又’若超過25(rc,則促使硫酸錢分解,考 慮裝置之腐姓而事先所進行的乾燥變得無意義。 接著,將經混合之廢研磨賴料或薄片進行加熱而培燒 097137448 200925112 35,藉此職可雜之贿稀土 4〇。 >作為加熱L燒35之裝置並無特別限定,可應用箱形爐、 旋轉爐、隧道爐等之—般锻燒爐。又於後述步驟⑺及⑻ 中,由於彻於輕步驟所產生之氨氣體使碳酸氫錄再生, 故較佳係具備排氣吸收槽等作為吸收所產生之氣體的設備。Oxide), other than Rare Earth Fluoride, is a mixture of ground glass materials, ground glass, enamel fiber, and other foreign matter. The composition of the waste abrasive slurry 10 varies depending on the process conditions used, but is usually discharged from the grinding step 9 in a state of about 5 to 50% by weight of the solid content. The composition is the conversion amount of the rare earth oxide based on the dry product. TRE0 (= (total bauxite oxide mass / total oxide mass) χ 100)) is 82 mass% (in which about 25 is a gasified rare earth component) The crushed compound is about 5 ❹% by mass of the aluminum compound or the iron compound is about 1% by mass, and other foreign materials such as glass frit or mat fiber are mixed. The waste abrasive slurry 1 is in the polishing step 9, and the abrasive slurry which is recycled while being recycled is finally condensed by gravity sedimentation to prepare a gasified rare earth D conversion (T_(Total) Rare Earth Oxide)) is a slurry of about 3% by mass. When the concentrate is concentrated by the gravity sedimentation method, the waste slurry may be separately used, but the commercially available polymer flocculant may be used to carry out the sedimentation more effectively. This becomes the starting material for the spent abrasive slurry treated by step (1). (First Step [I]) The first step [I] includes the following steps (1) to (5). (Step (1)) (Transfer the rare earth element in the waste grinding (4) material to obtain a rare earth solution 097137448 200925112 First, a waste abrasive polymerization material is used in the reaction vessel, and a certain amount of sulfur is added thereto. The compound (4) (hereinafter sometimes referred to as "ammonium sulfate or the like") 20 is used as a reaction reagent, and is mixed under mixing. Thereafter, it is formed into a sheet (1) in a drying step 33 and a calcination step 35. Waste abrasives. ❹ • The shape should be qualified, and there is no limit. It is more suitable for the type of sulphuric acid compound which has at least the means of introduction of waste abrasives, ammonium sulfate, etc. The amount of addition is about 40 parts, 60 parts, preferably about 5 parts, relative to the waste abrasive material (P(4). If the amount is less than 40 parts, the insoluble content of the rare earth element is increased, and If more than 6 parts are added, the above effects cannot be exerted, and it is not preferable to increase the amount of the wasted drug. Further, as the sulfuric acid compound, hydrogen sulfate can be used in addition to sulfuric acid. The mixed slurry can be I [transfer to the domain step 35 However, if it is considered that the device brain or the like is heated at a temperature, it is preferable to perform drying in advance = water. The spear is not particularly limited as a drying device, and a box drier, a dryer, and a vacuum drying H can be applied. If any of the Hi degrees is preferably (9) _25 generations ^ particularly good is 90-20 (TC. If the drying temperature is lower than _, it is not good in terms of drying efficiency, and 'if it exceeds 25 (rc, it promotes sulfuric acid money) Decomposition, considering the rot of the device, the drying performed in advance becomes meaningless. Next, the mixed waste abrasive or sheet is heated and fired 097137448 200925112 35, whereby the rare earth can be used. > The apparatus for heating the L-fired 35 is not particularly limited, and a general-purpose calcining furnace such as a box furnace, a rotary furnace, or a tunnel furnace can be applied, and in the steps (7) and (8) described later, the lightening step is performed. Since ammonia gas reproduces hydrogencarbonate, it is preferable to provide an apparatus such as an exhaust gas absorption tank as a gas generated by absorption.
❹ 加熱培燒35之溫度若為可藉上述反應形成硫酸稀土 4〇, 則無特別蚊,較佳為.1_°C之範圍,特佳為 c之範圍力未滿300 c ,則硫酸稀土之形成反應無法順利 進行:¾超過1000 C ’則成為反應所需以上之過剩溫度, 而由能量效率之觀點而言不佳。 接著,將藉加熱培燒35所生成之硫酸稀土 4〇㈣至反應 谷器(溶解裝置)中,添加水43進行溶解45。 作為反應容器,並無特別限定,較佳係至少具備攪拌手 段、加熱手段、硫酸稀土之導入手段的攪拌槽型者。若以同 一設備進行下一步驟(2)(ph調整步驟),則較佳係具備於步 驟(2)後述之pH調節劑之導入手段及碳酸氣體回收設備。 所添加之水的量,係相對於硫酸稀土 1〇〇份,較佳為 2000-10000 份、特佳 3000-9000 份。 在硫酸稀土對水之溶解差劣時,藉由添加少量硫酸、或將 含有不溶之硫酸稀土份的溶液進行加熱,則可促進其溶解。 又’亦可組合進行硫酸添加、溶液加熱。此時之硫酸添加量, 並無特別限定,較佳係相對於硫酸稀土 100份為1-2〇份、 097137448 12 200925112 特佳5-10份。作為加熱溫度,較佳為40-8(TC、特佳5〇〜7〇 °C。若結束硫酸稀土之溶解45,則得到酸性水溶液(以下有 時稱為「酸性溶液」)。 (步驟(2)) (自稀土類元素之酸性溶液(漿料)分離Si、A卜Fe不溶解 ^ 殘渣之步驟) '於結束步驟(1)之上述酸性溶液(酸性漿料)中,添加可溶 Ο 性之鹼成分作為pH調節劑50 ’調節pH53,使pH増加,藉 此可選擇性地僅使已溶解的二氧化矽(Si)、鋁(A1)、鐵(Fe) 成分析出成殘渣(或固體不需要成分)63。 作為pH調節時之pH條件,較佳係控制為pH4_7、更佳 PH5-6之範圍’最佳為pH5. 5。若未滿pH4,則Si、Ai、p 成分之總量不完全析出,又,若超過PH7,則由於發生Al Si成分之再溶解或稀土類元素之析出,故不佳。 © 作為PH調節劑50之可溶性鹼成分,並無特別限定,美本 上可應用驗金屬鹽、鹼土類金屬鹽、錄鹽或氨(水)等。此等 之中,由沉澱物之過濾性的觀點而言,較佳係使用碳酸職, 例如NaHC〇3、NazCO3、NIhHCO3等。於後述之步驟(6)中现, 進行廢液之回收時,特佳係使用氨水或銨鹽。 在 尚且,在於酸性之漿料中添加碳酸鹽之溶液作 > 劑50的情況’係因反應而生成、釋出二氧化碳氣體 體),溶液在外觀上呈沸騰狀態。因此,於反應器中,乳 較佳 097137448 13 200925112 係β又置迴流冷凝器’使釋出碳酸氣體(以及伴同之水蒸氣) 冷卻,僅將水蒸氣凝縮後,導入•回收至後述步驟(8)中之 礙酸氣體吸收裝置。 如以上般,於進行pH調節53後,將漿料一邊攪拌、一邊 進行冷卻’於3〇-5〇。〇左右之溫度條件下將沉澱之以二氧化 矽(Slllca)、氧化鋁(Alumina)及鐵(Iron)為主成分之溶解 殘渣63等作為固體不需要成分而藉過濾等之固液分離手段 ❹60予以分離,並予以廢棄65。基本上,二氧化矽、氧化鋁 成为之氫氧化物為難過濾性,但藉由析出為碳酸鹽,則可效 率佳地藉過濾等進行固液分離。過濾等之溫度並不一定限定 於上述範圍’但溫度若過高,則於作業環境上並不佳,故較 佳係於4〇〇c左右進行操作。 作為固液分離手段6〇,在過濾的情況,作為過濾裝置可 使用壓濾器、筒式過濾器或泵加壓式線路過濾器等。由安全 性的觀點而言,較佳係於設置在配管線路之線路過濾器内進 行泵循環而進行處理。又,配合過濾分離之情況、處理量或 固體之過濾性等,可使用濾布、陶瓷過濾器、濾紙等適當之 濾布。 如此’於步驟(2)中,以不溶解成分(殘渣)之型式去除固 體雜質(固體不需要成分),取出溶解了稀土類元素之酸性水 溶液。 (步驟(3)) 097137448 14 200925112 (自稀土類溶液生成•晶析出碳酸稀土的步驟) 將如此所得之稀土類元素(硫酸稀土)之酸性水溶液70導 入至適當之反應器中,添加沉澱劑(晶析劑)、例如碳酸氫銨 73 ’使其生成•晶析8〇為碳酸稀土,而形成含碳酸稀土之 聚料83 ’同時使碳酸氣體85發散。 作為沉殿劑,基本上使用錢鹽、鹼金屬之碳酸鹽、驗土類 金屬之碳酸鹽、鹼金屬之碳酸氫鹽或鹼土類金屬之碳酸氫鹽 ® 中之至少一種以上,但藉由使用碳酸氫銨(NH4HC〇3)作為沉澱 劍’可得到過濾性及洗淨性良好之碳酸稀土結晶。從而,以 下說明係針對碳酸氫銨進行敘述,但亦可直接應用其他沉澱 劑。 作為反應容器並無特別限定,較佳係具備該酸性水溶液 70及碳酸氫銨73之導入手段、攪拌手段、加熱手段等的攪 拌槽型反應器。又,由於藉反應使二氧化碳氣體(碳酸氣體) 生成、釋出,故較佳係設置迴流冷凝器,使釋出碳酸氣體(以 及伴同之水蒸氣)冷卻,僅將水蒸氣凝縮後,導入•回收至 後述步驟(8)中之碳酸氣體吸收裝置。 所添加之姐氫狀形態或濃度絲任何蚊,可依水容 液或漿料狀態進行添加,由操作性的觀點而言,特佳係作办 濃度5-10%範圍之碳酸氫銨水溶液而使用。 ’、成 碳酸氫銨73之添加量’若為足夠使酸性水溶液之酸 進行中和的量即可,該量·步驟⑴之㈣磨騎(或^ 097137448 15 200925112 磨劑中之稀土成分量)每100份中,較佳為以乾燥品基準計 添加20-50份、更佳30-40份。 碳酸氫銨73對於酸性水溶液70之添加,係為了使反應所 生成之碳酸氣體更順利地自系統發散,故較佳係儘可能地於 高溫下進行。通常係例如於加熱手段之反應器之被套中,循 環80C左右的熱水,於一邊加熱、一邊攪拌之條件下,歷 ' 時2-3小時實施碳酸氫銨之分割添加。 ❹(步驟(4)) (碳酸稀土之分離步驟) 將上述含有碳酸稀土之漿料83 ,冷卻至6〇艽以下、較佳 3〇~50°C後,於固液分離步驟87中,藉由例如過濾使碳酸稀 土 89與銨鹽(例如硫酸銨水溶液)(濾液)90分離。所分離之 碳酸稀土較佳係進一步以依質量計為卜3倍量左右的水進 行洗淨’藉此抑制作為附著母液所伴同的廢研磨劑漿料中之 ❹雜質的知m,為了更充分地騎洗淨,可將經分離之 魏稀土之賴再:欠分散(repulp)於水中作成漿料,重複進 行固液分離操作之操作。如此,於步驟⑷中,所生成之碳 酸稀土係藉由過濾、洗淨’而被分離、精製。又,此處所指 之固液分離87係包括n洗淨之操作。 (步驟(5)) (碳酸稀土之烺燒步驟) 將於步驟⑷經’分離(職•洗淨)之碳酸稀土 89,進 097137448 16 200925112 行乾燥•烺燒100,作成氧化稀土 105。 作為乾燥設備並無特別限定,係使用箱形乾燥器、帶式乾 燥器、真空乾燥器等任意者。乾燥溫度較佳為6〇_25〇°c、 特佳90-20(TC。作為煅燒設備並無特別限定,係使用箱型 爐$疋轉爐、隧道爐等任意者。作為烺燒溫度,係於大氣環 士兄中為 3〇〇-1200 C、較佳 400-1100°C、更佳 500-1 〇〇〇。〇, 煅燒時間為進行1-24小時左右、較佳3-20小時左右。又, 〇 於此雖分別記述乾燥•煅燒,但亦可使用緞燒設備同時進行 乾燥·煅燒。 尚且,於煅燒時係因反應而釋出二氧化碳氣體(碳酸氣 體)85。因此,較佳係於煅燒設備中合併設置排氣吸收設備, 將釋出碳酸氣體冷卻後’導入•回收至後述步驟(8)中之碳 酸氣體吸收裝置中。 煅燒所得之稀土類氧化物(氧化稀土)1〇5,係作成回收氧 ❹ 化稀土,於解碎後投入至一般之研磨劑製造線之微粒化處理 步驟中,再利用作為研磨劑之原料。 以上屬於第一步驟[I]。亦即,於步驟[I]中實施步驟 (1)-(5),自含有稀土類元素之氧化物的廢研磨劑漿料回收 該稀土類氧化物。 (第二步驟[II]) 其次,敘述第二步驟[II]。步驟[II]中,係實施以下之步 驟(6),將於第一步驟[I]使用作為形成碳酸稀土所需之反應 097137448 200925112 劑的硫酸化合物、較佳硫酸錢回收,將該回收之硫酸鐘再利 用於上述第—步驟[1]。又,關於硫酸㈣收時所產生之水, 亦視需要作為回收水’再利用作為使上述第ι步鱗⑴之硫 酸稀土溶解的溶媒。 (步驟(6)) (硫酸銨及水之回收步驟) 於上辭驟⑶中,係藉下式⑴之反應,副產生出所投入 ❹之碳酸氫録之1/2莫耳量的硫酸錢。此係於步驟⑷將碳酸 稀土進拥好離時,作成2〜_度之雜聽液而排出 至滤液中。將此濾峡行蒸鱗之濃縮分離分離回收成高 濃度之硫酸銨水溶液與水。❹ If the temperature of the heated simmering 35 is such that the above reaction can form rare earth sulphate 4 〇, there is no special mosquito, preferably in the range of .1 ° ° C, especially preferably in the range of c less than 300 c, then the rare earth sulfate The formation reaction does not proceed smoothly: 3⁄4 over 1000 C' is the excess temperature required for the reaction, and is not good from the viewpoint of energy efficiency. Next, the rare earth sulfate 4(4) produced by heat-burning 35 is heated to a reaction barn (dissolving device), and water 43 is added to dissolve 45. The reaction container is not particularly limited, and is preferably a stirred tank type including at least a stirring means, a heating means, and a means for introducing rare earth sulfate. When the next step (2) (ph adjustment step) is carried out by the same apparatus, it is preferable to provide the introduction means of the pH adjuster and the carbonic acid gas recovery apparatus which will be described later in the step (2). The amount of water added is preferably from 2,000 to 10,000 parts, particularly preferably from 3,000 to 9000 parts, based on 1 part by weight of the rare earth sulfate. When the dissolution of the rare earth sulfate to water is poor, the solution can be promoted by adding a small amount of sulfuric acid or heating a solution containing the insoluble sulfuric acid rare earth. Further, sulfuric acid addition or solution heating may be combined. The amount of sulfuric acid added at this time is not particularly limited, but is preferably 1-2 parts by weight with respect to 100 parts of rare earth sulfate, and 5-10 parts by 097137448 12 200925112. The heating temperature is preferably 40-8 (TC, particularly preferably 5 〇 to 7 〇 ° C. When the dissolution of the rare earth sulfate 45 is completed, an acidic aqueous solution (hereinafter sometimes referred to as "acid solution") is obtained. 2)) (Step of separating Si, A, Fe, and insoluble from the acidic solution (slurry) of the rare earth element) 'In the above acidic solution (acidic slurry) of the end step (1), adding soluble cesium The alkali component is used as a pH adjuster 50' to adjust pH53 to increase the pH, thereby selectively analyzing only dissolved ceria (Si), aluminum (A1), and iron (Fe) into a residue ( Or the solid does not require a component. 63. As a pH condition for pH adjustment, it is preferably controlled to a pH of 4-7, more preferably a range of PH5-6. The pH is preferably 5. 5. If the pH is less than 4, the components of Si, Ai, and p are When the amount exceeds pH 7, the re-dissolution of the Al Si component or the precipitation of the rare earth element occurs, which is not preferable. The soluble alkali component of the pH adjuster 50 is not particularly limited. This can be applied to the detection of metal salts, alkaline earth metal salts, salt or ammonia (water), etc. From the viewpoint of the filterability of the precipitate, it is preferred to use a carbonated member such as NaHC〇3, NazCO3, NIhHCO3, etc. In the step (6) described later, when the waste liquid is recovered, it is particularly preferable to use ammonia water or Further, in the case where the carbonate solution is added to the acidic slurry as the > agent 50, 'the carbon dioxide gas body is formed by the reaction, and the solution is in a boiling state in appearance. Therefore, in the reactor, the milk is preferably 097137448 13 200925112, and the reflux condenser is set to cool the released carbonic acid gas (and the accompanying water vapor), and only the water vapor is condensed, and then introduced and recycled to the later step (8). In the acid gas absorption device. As described above, after the pH adjustment 53 was carried out, the slurry was cooled while stirring, at 3 〇 -5 Torr. A solid-liquid separation means for filtering, such as a solid residue component, which is precipitated by using cerium oxide (Slllca), alumina (Alumina), and iron (Iron) as a solid component, under a temperature condition of about 〇60 Separate and discard 65. Basically, the hydroxide which is made of cerium oxide or aluminum oxide is difficult to filter, but by precipitation as a carbonate, solid-liquid separation is possible by filtration or the like with good efficiency. The temperature such as filtration is not necessarily limited to the above range. However, if the temperature is too high, it is not preferable in the working environment, so it is preferable to operate at about 4 °C. As the solid-liquid separation means 6 〇, in the case of filtration, a filter press, a cartridge filter, a pump pressurized line filter or the like can be used as the filtration device. From the viewpoint of safety, it is preferable to carry out a pump cycle in a line filter provided in a piping line for processing. Further, an appropriate filter cloth such as a filter cloth, a ceramic filter or a filter paper can be used in combination with the filtration separation, the treatment amount, or the filterability of the solid. In the step (2), solid impurities (solid unnecessary components) are removed in a form of insoluble components (residues), and an acidic aqueous solution in which rare earth elements are dissolved is taken out. (Step (3)) 097137448 14 200925112 (Step of forming a rare earth solution or crystallization of rare earth carbonate) The acidic aqueous solution 70 of the rare earth element (rare earth sulfate) thus obtained is introduced into a suitable reactor, and a precipitant is added ( A crystallization agent, for example, ammonium hydrogencarbonate 73' is formed to crystallize 8 〇 to be a rare earth carbonate, and a rare earth carbonate-containing aggregate 83' is formed to simultaneously disperse the carbonic acid gas 85. As a sinking agent, at least one of a money salt, an alkali metal carbonate, a soil-based metal carbonate, an alkali metal hydrogencarbonate or an alkaline earth metal hydrogencarbonate® is basically used, but by using Ammonium hydrogencarbonate (NH4HC〇3) is used as a precipitation sword to obtain a rare earth carbonate crystal having good filterability and detergency. Therefore, the following description is directed to ammonium hydrogencarbonate, but other precipitants may be directly applied. The reaction vessel is not particularly limited, and is preferably a stirred tank type reactor including an introduction method of the acidic aqueous solution 70 and ammonium hydrogencarbonate 73, a stirring means, and a heating means. Further, since carbon dioxide gas (carbonic acid gas) is generated and released by the reaction, it is preferable to provide a reflux condenser to cool the carbon dioxide gas (and the accompanying water vapor), and only to condense the water vapor, and then introduce and recycle it. The carbon dioxide gas absorption device in the step (8) described later. The added hydrogen form or concentration of any mosquito can be added according to the water content or the state of the slurry. From the viewpoint of operability, it is particularly suitable for the aqueous solution of ammonium hydrogencarbonate having a concentration of 5-10%. use. ', the amount of ammonium bicarbonate 73 added' may be an amount sufficient to neutralize the acid of the acidic aqueous solution, the amount of the step (1) (four) grinding ride (or ^ 097137448 15 200925112 the amount of rare earth components in the grinding agent) It is preferable to add 20-50 parts, more preferably 30-40 parts per 100 parts of the dry product. The addition of the ammonium hydrogencarbonate 73 to the acidic aqueous solution 70 is preferably carried out at a high temperature as much as possible in order to allow the carbonic acid gas generated by the reaction to diffuse more smoothly from the system. Usually, for example, in a jacket of a reactor of a heating means, a hot water of about 80 C is circulated, and while stirring and heating, the division of ammonium hydrogencarbonate is carried out for 2-3 hours. ❹ (Step (4)) (Separation step of rare earth carbonate) The slurry containing the rare earth carbonate 83 is cooled to 6 Torr or less, preferably 3 〇 to 50 ° C, and then borrowed in the solid-liquid separation step 87. The rare earth carbonate 89 is separated from the ammonium salt (for example, aqueous ammonium sulfate solution) (filtrate) 90 by, for example, filtration. It is preferable that the separated rare earth carbonate is further washed with water of about 3 times by mass, thereby suppressing the impurity m in the waste abrasive slurry accompanying the adhesion of the mother liquid, in order to more fully The ground ride is washed, and the separated Wei rare earth slag can be further repulped in water to form a slurry, and the operation of the solid-liquid separation operation is repeated. Thus, in the step (4), the generated rare earth carbonate is separated and purified by filtration and washing. Further, the solid-liquid separation 87 referred to herein includes an operation of n washing. (Step (5)) (Step of calcining rare earth carbonate) The rare earth carbonate 89 which is subjected to the separation in the step (4) is dried in the 097137448 16 200925112 line and dried to 100% to form the rare earth oxide 105. The drying device is not particularly limited, and any one of a box dryer, a belt dryer, and a vacuum dryer is used. The drying temperature is preferably 6 〇 _25 〇 ° c, and particularly preferably 90 -20 (TC. The calcining equipment is not particularly limited, and any one of a box type furnace, a tunnel furnace, and the like is used. It is 3〇〇-1200 C, preferably 400-1100 ° C, more preferably 500-1 〇〇〇 in the atmosphere ring brother. 〇, the calcination time is about 1-24 hours, preferably about 3-20 hours. Further, although drying and calcination are described separately, drying and calcination may be simultaneously performed using a satin burning apparatus. Further, carbon dioxide gas (carbonic acid gas) 85 is released by the reaction during calcination. The exhaust gas absorbing device is combined in the calcining apparatus, and the released carbonic acid gas is cooled, and then introduced and recovered into the carbonic acid gas absorption device in the step (8) described later. The rare earth oxide (rare earth oxide) obtained by calcination is 1〇5. It is used to recover the oxidized rare earth, and after being pulverized, it is put into the micronization treatment step of the general abrasive production line, and then used as a raw material of the abrasive. The above is the first step [I]. That is, in the step Steps (1)-(5) are implemented in [I], self-contained The rare earth oxide is recovered from the waste abrasive slurry of the oxide of the earth element. (Second step [II]) Next, the second step [II] is described. In the step [II], the following steps are carried out (6) ), in the first step [I], the sulfuric acid compound, preferably sulfuric acid, which is the reaction required to form the rare earth carbonate 097137448 200925112, is recovered, and the recovered sulfuric acid clock is reused in the above-mentioned first step [1]. The water produced by the sulfuric acid (IV) is also used as a solvent for dissolving the rare earth sulfate in the first step (1) as the recovered water. (Step (6)) (Step of recovering ammonium sulfate and water) In the above-mentioned remarks (3), by the reaction of the following formula (1), the sulphuric acid money recorded by the carbon dioxide charged in the hydrazine is produced by the sub-type (1). This is done in the step (4) when the rare earth carbonate is contained. The mixed liquid of 2 to _ degrees is discharged into the filtrate, and the concentrated condensed scale is separated and separated into a high concentration aqueous solution of ammonium sulfate and water.
Ln2(S〇4)3+6HN4HC〇3^Ln2(C〇3)3| + 3(NH〇2S〇4 + 3C〇2 f + 3H2〇 (1) (式(1)中,Ln表示稀土類元素。) 〇 ⑹上述’含有碳酸稀土之聚料83係藉固液分離87分離為 碳酸稀土 89與硫酸銨水溶液(滤液)9〇。將該含有硫酸錢之 滤液90於濃縮分離步驟93巾,藉漢縮分離分別分離•回收 硫酸銨20與水43。 作為濃縮分離93之方法並錢別限^,可使用蒸顧濃 縮、真空濃縮等。藉由喷霧乾燥H、其他乾燥設備,可使其 完全乾固而回收’但若考慮所回收之硫酸錢之使用形態,將 硫酸銨以溶液狀回收者係由能量效率方面而言屬較佳。作為 097137448 200925112 回收硫酸銨溶液之濃度並無特別限定,較佳為3〇〜7〇質量 %、特佳40〜60質量%。 作為實際之濃縮分離裝置,較佳可使用具備有冷凝器(凝 縮器)的蒸發罐。亦即,濾液90係供給至蒸發罐之鍋中,將 藉加熱而蒸發之水43c凝縮並回收,可使用作為於步驟(2) 中用於溶解硫酸稀土 40之水(或至少其一部分)43。另一方 面,自該鋼回收所濃縮之硫酸錢溶液2〇c,可使用作為步驟 ❹ (1)中之反應藥劑的硫酸銨20。 (第三步驟[ΠΙ]) 接著敘述步驟[III]。於步驟[UI]中,實施以下之步驟 α)~(8),使於第1步驟[I]中使用作為碳酸稀土之沉澱劑的 碳酸氫銨73再生,並將該再生碳酸氫銨再利用於上述第i 步驟[I]。 (步驟(7)) ❹(氨之回收步驟) 於上述步驟(1)之加熱培燒步驟35中,添加作為反應藥劑 之硫酸化合物的硫酸銨20中之氨成分係以氣體(NH3)型式產 •生。又,此時,研磨劑中所含有之氟成分亦同時以氟氣 之型式產生。於排氣吸收步驟112中將此等氣體(F2/NH3)4 收至水或水溶液中,作成氟化銨水溶液,並自其沉殿去除氣 成分,回收氨水。 亦即,於如上述所回收之氟化銨水溶液中,添加沉澱劑 097137448 19 200925112 110使氟成分沉澱。作為所添加之沉澱劑11()並無特別限 疋’但較佳係使用可使氟成分以溶解度低之鈣鹽之型式進行 /冗/殿回收之具詞成分的鹽,例如氫氧化妈、碳酸弼等。如 此,氟成分成為氟化鈣而沉澱、過濾115,作為殘渣117而 廢棄119。另一方面,氨水κο雖呈游離,但將其於其次之 步驟(8)中使用於碳酸氣體之反應吸收(碳酸化反應)13〇。 • (步驟(8)) 〇 (碳酸氣體之回收及碳酸氫銨之合成步驟) 於步驟(2)之pH調整步驟53、步驟(3)之碳酸稀土生成· 晶析步驟80及步驟(5)之煅燒步驟1〇〇中,自反應器等所排 出之碳酸氣體係藉上述步驟(7)所回收之氨水溶液而被反應 吸收(Gas Absorption Accompanied by Chemical React ion)(碳酸化反應(Carbonat ion) )130’ 藉下式(2)以碳 酸氫銨73之型式被回收。 ❹ HN3 + H2〇 + C〇2—HN4HC〇3 (2) 反應吸收之液溫度係控制在10〜40t、較佳20〜30¾之範 圍。吸收該碳酸氣體並形成碳酸氫銨的裝置,可為一般吸收 塔方式,但由於亦有析出局部性濃縮之碳酸氫銨的情況,故 較佳為攪拌槽形式。 亦即,作為進行反應吸收之反應容器R,較佳係如圖2所 示之具備碳酸氣體導入手段1、攪拌手段2、溫度調節手段 3、冷凝器4、逆流接觸式(Counter Current)吸收塔5的授 097137448 20 200925112 摔式吸收裝置。又’ 6係將氨水溶液進行濃度調節之反應吸 收用氨水。而且,較佳係將前段之攪拌式吸收裝置,盥 之層板塔mate Tower)或填充塔(Packed T〇we〇 '濕壁塔 (Wetted Wali 了謝)¥之魏_方核祕予以組合使 用。又’視需要供給新鮮之碳酸氣體或稀釋水而將液中之碳 酸氫銨濃度控制在屬於飽和溶解度以下之5~25質量%、較佳 8〜10質量%的範圍。該濃度若過低,則吸收裝置之設備負荷 ❹變尚,又,若濃度過高,則由於形成碳酸氫銨漿料,故較佳 係控制於此範圍内。 作為攪拌式吸收裝置,可採用附攪拌翼之分次式、連續次 之任一種,亦可為裝備了錨、渦輪、槳、全區Gullz〇ne) 翼等的槽型吸收裝置’可由市售之攪拌式氣體吸收設備予以 適當選擇。 藉由與氨水溶液(反應吸收用氨水6)之反應吸收而生成 〇之碳酸氫銨73之溶液,係暫時貯藏(st〇ck)於中間槽後,供 給至步驟(3)之碳酸稀土生成•晶析步驟8〇,適合再利用作 為使礙酸稀土類生成的晶析劑。 (發明效果) 如以上所詳述,根據本發明,係提供一種自研磨速度大幅 降低而通常被廢棄之含有鈽等之稀土類元素的廢研磨劑漿 料’回收稀土類70素的方法,對於該廢研磨劑漿料,可使用 硫酸敍等硫酸化合物作為反應藥劑而使氧化稀土成分選擇 097137448 200925112 性地溶解為硫酸稀土。 另外’將經溶解之氧化稀土成分,以碳酸稀土之型式進行 分離•回收時’預先以特定之ρΙί進行固液分離,藉此將溶 解共存之鐵離子等之雜質選擇性地分離出為不溶固體成 分’藉此’得到可再利用作為研磨劑原料之高純度碳酸稀 • 土’將此進行緞燒而可容易地回收氧化稀土。 .再者’根據本發明,於將含有稀土類氧化物之漿料與反應 ❹ 藥劑之硫酸銨等之硫酸化合物混合,並加熱焙燒,藉此作成 硫酸稀土並使其溶解於水。接著,以pH調節劑調整為特定 pH,預先將鐵離子等之雜質予以固液分離後,於選擇性地溶 解有氧化稀土成分之該酸性水溶液中,添加碳酸氫銨作為沉 殿劑而使其反應,使碳酸稀土生成、晶析。此處所使用之 pH調節劑及沉澱劑為氨水或銨鹽時’並不需要將於該反應 步驟所副產生出之硫酸銨及水廢棄,可回收、再利用作為上 ❹ 述反應藥劑及溶媒。 另外,將於上述加熱焙燒步驟所產生之氨氣體回收,與於 pH調節步驟、晶析步驟及烺燒步驟所產生之碳酸氣體反 應,作為碳酸氫銨,藉此可回收使用高價之碳酸氫銨,且步 驟廢液之無害化處理變得簡易。 [實施例] 以下,藉實施例說明本發明。其中,此等僅為實施態樣之 一例(Exemplary Embodiment of the Invention) ’ 本發明 097137448 22 200925112 之技術範圍(涵括本發明之權利範圍),並不由此等實施例進 行限定性或限雜的解釋。又,在未制限定之下,%為質 里%。又’實施例中之處理操作係依照圖1之絲圖進行。 [實施例1] (1)(將廢研磨劑漿料之稀土類元素溶解,得到稀土類溶液的 > 步驟(1)) .起始原料之廢研磨劑漿料10係如以下般所調製者。亦 ❹即,採取藉玻璃碟之研磨所生成之廢研磨劑漿料並進行重力 沉降處理,調整為乾燥基準下之固形份濃度為約別質量% 的漿料0 尚且,採取該漿料之一部分,於空氣中丨卯亡之條件下針 對經乾燥1日夜的粉體依螢光x射線法(x_ray Fluorescence Analysis)所求得之成分元素的量,係表i 所示之結果。 ❹表1 (廢研磨劑漿料之組成(乾燥品基準)) 成分 濃度(質量%) TRE0 78.4 Si〇2 3. 6 AI2O3 1.0 Fe2〇3 6.9 097137448 23 200925112 F -—-一 -- 5.2 其他 4.9 首先’進行將上述廢研磨劑漿料與屬於反應藥劑之硫酸銨 混合之操作。將該漿料lkg採取至3L的燒杯 添加硫酸 銨426g。接著以約i5〇rpm之速度於授拌混合i •J、〇 將上述漿料在箱型乾燥機中於空氣中90〇C之條件下乾燥 24小時,得到乾燥物760g。 Ο 將上述乾燥物於小型電爐中,依50(TC、6小時進行加熱 培燒’得到硫酸稀土 520g。 ”、 此時所產生之氟氣體、氨氣體係被吸收至水溶液中而作成 氟化銨水溶液,於後述之步驟(7)中,回收氨,對於氟成分 則以氟化鈣之型式進行回收•廢棄。 將上述硫酸稀土溶解於20L之水中,得到稀土類元素 性溶液。 ' 〇 (2)(自稀土類元素之酸性溶液(浆料)分離含有Si、A卜Fe 之未溶解殘渣,步驟(2)) 、二於所彳于之酸性溶液(漿料)中,在120rpm之授拌條 件下,添加作為pH調整劑之1〇%濃度之碳酸氫銨溶液,將 調整為PH5.5,並攪拌!小時。 此時,於中和反應所生成之碳酸氣體係隨水蒸氣被發散, /合液於外觀上呈沸騰狀態’故以迴流冷凝器進行冷卻而使水 !氣凝縮後’導人至後述步驟⑻之碳酸氣體吸收裝置而以 097137448 24 200925112 氨進行反應吸收’回收作為碳酸氫錢。 其次,以内徑300mm φ之Nutsche式吸引過遽器,使用 濾紙(AdvanteCh東洋公司製)將未溶解成分固液分離成為 固體不需減分’雜解了稀土類元权械雜水溶液回 收。 ㈣狀固形份(殘奸關*需成分)之乾燥品基準的 質量為75g ’由螢光X射線法所進行之分析,確認其成分為 ❹ 二氧化梦、銘、鐵。 (3)(自稀土類溶液使碳酸稀土生成、晶析:步驟(3)) 將溶解了經滤別之稀土類元素的酸性水溶液,於12㈣m 之攪拌條件下,加溫至約6(rc。其次,逐次添加約2〇質量 %濃度之破酸氫錄之溶液2〇〇〇g,並逐次進行下式(1)之反 應’使碳酸稀土之結晶生成•晶析出。Ln2(S〇4)3+6HN4HC〇3^Ln2(C〇3)3| + 3(NH〇2S〇4 + 3C〇2 f + 3H2〇(1) (In the formula (1), Ln represents a rare earth Element (6) The above-mentioned 'polycarbonate containing rare earth 83 is separated into a rare earth carbonate 89 and an aqueous solution of ammonium sulfate (filtrate) by solid-liquid separation 87. The filtrate 90 containing sulfuric acid is subjected to concentration separation step 93, Separation and recovery of ammonium sulfate 20 and water 43 by separation of Hans. As a method of concentration separation 93, it is possible to use distillation, concentration, vacuum concentration, etc. by spray drying H, other drying equipment, It is completely dried and recovered. However, considering the use form of the recovered sulfuric acid, it is preferable to use ammonium sulfate as a solution in terms of energy efficiency. As a concentration of 097137448 200925112, the recovery of ammonium sulfate solution is not particularly high. Preferably, it is preferably 3 〇 to 7 〇 mass%, particularly preferably 40 to 60 mass%. As the actual concentration separation device, it is preferable to use an evaporation canister equipped with a condenser (condenser). It is supplied to the pot of the evaporation can, and the water 43c evaporated by heating is condensed and recovered. The water (or at least a part thereof) 43 for dissolving the rare earth sulfate 40 in the step (2) is used. On the other hand, the concentrated sulfuric acid solution 2 〇c is recovered from the steel, and can be used as the step ❹ (1) Ammonium sulfate 20 of the reaction reagent in the middle (third step [ΠΙ]) Next, the step [III] is described. In the step [UI], the following steps α) to (8) are carried out, and the first step [I] is performed. The ammonium hydrogencarbonate 73 which is a precipitant of rare earth carbonate is used for regeneration, and the regenerated ammonium hydrogencarbonate is reused in the above i-th step [I]. (Step (7)) ❹ (Ammonia recovery step) In the heating and calcining step 35 of the above step (1), the ammonia component of ammonium sulfate 20 added as a sulfuric acid compound as a reaction agent is produced in a gas (NH3) type. • Health. Further, at this time, the fluorine component contained in the polishing agent is simultaneously produced in the form of fluorine gas. The gas (F2/NH3)4 is taken up in water or an aqueous solution in the exhaust gas absorption step 112 to form an aqueous ammonium fluoride solution, and the gas component is removed from the sinking chamber to recover the ammonia water. Namely, a precipitant 097137448 19 200925112 110 was added to the aqueous ammonium fluoride solution recovered as described above to precipitate a fluorine component. The precipitant 11 () to be added is not particularly limited, but it is preferably a salt which can be used as a component of a calcium salt having a low solubility in a low solubility, such as a hydroxide, Barium carbonate and the like. Thus, the fluorine component precipitates as calcium fluoride, and is filtered 115, and 119 is discarded as residue 117. On the other hand, although the ammonia water κ is free, it is used in the next step (8) for the reaction absorption (carbonation reaction) of carbonic acid gas 13 〇. • (Step (8)) 〇 (recovery of carbonic acid gas and synthesis of ammonium bicarbonate) pH adjustment step 53 in step (2), rare earth carbonate formation in step (3), crystallization step 80 and step (5) In the calcination step 1 , the carbon dioxide gas discharged from the reactor or the like is absorbed by the ammonia aqueous solution recovered in the above step (7) (Gas Absorption Accompanied by Chemical Recation) (Carbonation) ) 130' is recovered in the form of ammonium hydrogencarbonate 73 by the following formula (2). ❹ HN3 + H2〇 + C〇2—HN4HC〇3 (2) The temperature of the liquid absorbed by the reaction is controlled in the range of 10 to 40 t, preferably 20 to 303⁄4. The apparatus for absorbing the carbonic acid gas to form ammonium hydrogencarbonate may be a general absorption tower type. However, since the locally concentrated ammonium hydrogencarbonate is also precipitated, it is preferably in the form of a stirring tank. That is, as the reaction container R for performing reaction absorption, as shown in FIG. 2, it is preferable to provide the carbonation gas introduction means 1, the stirring means 2, the temperature adjustment means 3, the condenser 4, and the counter current absorption tower (Counter Current) absorption tower. 5 097137448 20 200925112 drop absorption device. Further, the 6-series ammonia water was used for the reaction-adjusted ammonia aqueous solution. Moreover, it is preferred to combine the agitating absorption device of the preceding stage, the mate tower of the slab or the packed tower (Packed T〇we〇' Wet Wall Tower (Wetted Wali)) Further, 'the concentration of ammonium bicarbonate in the liquid is controlled to be 5 to 25% by mass, preferably 8 to 10% by mass or less, which is below the saturated solubility, if necessary, to supply fresh carbonic acid gas or dilution water. If the concentration is too low The equipment load of the absorption device is changed, and if the concentration is too high, since the ammonium hydrogencarbonate slurry is formed, it is preferably controlled within this range. As the stirring type absorption device, the stirring wing can be used. The tank type absorption device equipped with an anchor, a turbine, a paddle, a full-length Gullz〇ne wing, etc. can be appropriately selected from commercially available agitated gas absorption devices. The solution of ammonium hydrogencarbonate 73 is formed by absorption reaction with an aqueous ammonia solution (ammonia water for reaction absorption 6), and is temporarily stored in the intermediate tank and then supplied to the rare earth carbonate in the step (3). The crystallization step 8 is suitable for reuse as a crystallization agent for forming an acid-resistant rare earth. (Effect of the Invention) As described in detail above, according to the present invention, there is provided a method for recovering rare earth 70, which is a waste abrasive slurry containing a rare earth element such as cerium, which is usually discarded since the polishing rate is greatly reduced. In the waste abrasive slurry, a sulfuric acid compound such as sulfuric acid can be used as a reaction agent to selectively dissolve the rare earth oxide component 097137448 200925112 into rare earth sulfate. In addition, when the dissolved rare earth oxide component is separated and recovered in the form of rare earth carbonate, it is subjected to solid-liquid separation in advance, thereby selectively separating impurities such as dissolved iron ions into insoluble solids. The component 'by this' is obtained as a high-purity carbonic acid rare earth which can be reused as an abrasive raw material, and this can be satin-fired to easily recover the rare earth oxide. Further, according to the present invention, a rare earth oxide-containing slurry is mixed with a sulfuric acid compound such as ammonium sulfate of a reaction hydrazine, and calcined by heating to form a rare earth sulfate and dissolved in water. Then, the pH adjuster is adjusted to a specific pH, and impurities such as iron ions are subjected to solid-liquid separation in advance, and then ammonium hydrogencarbonate is added as a sinking agent to the acidic aqueous solution in which the rare earth oxide component is selectively dissolved. The reaction generates and crystallizes rare earth carbonate. When the pH adjuster and the precipitant used herein are ammonia or an ammonium salt, it is not necessary to discard ammonium sulfate and water which are produced by the reaction step, and it can be recovered and reused as the above-mentioned reaction agent and solvent. In addition, the ammonia gas generated in the above calcination step is recovered, and reacted with the carbonic acid gas generated in the pH adjustment step, the crystallization step, and the calcination step, as ammonium hydrogencarbonate, whereby high-priced ammonium bicarbonate can be recovered. And the harmless treatment of the step waste liquid becomes easy. [Examples] Hereinafter, the present invention will be described by way of examples. However, these are only the technical scope of the invention 097137448 22 200925112 (including the scope of the present invention), and are not limited or limited by the embodiments. Explanation. Also, under the unrestricted limit, % is the quality %. Further, the processing operation in the embodiment is carried out in accordance with the wire pattern of Fig. 1. [Example 1] (1) (The rare earth element of the waste abrasive slurry was dissolved to obtain a rare earth solution > Step (1)) The waste abrasive slurry 10 of the starting material was prepared as follows. By. In other words, the waste abrasive slurry generated by the grinding of the glass dish is subjected to gravity sedimentation treatment, and the slurry having a solid content concentration of about 3% by mass is adjusted to be a dry basis, and a part of the slurry is taken. The amount of the component elements obtained by the x-ray Fluorescence Analysis of the dried 1 day and night under the condition of death in the air is the result shown in Table i. ❹ Table 1 (Composition of waste abrasive slurry (dry product basis)) Component concentration (% by mass) TRE0 78.4 Si〇2 3. 6 AI2O3 1.0 Fe2〇3 6.9 097137448 23 200925112 F -—-一-- 5.2 Others 4.9 First, an operation of mixing the above-mentioned waste abrasive slurry with ammonium sulfate belonging to the reaction agent is carried out. The slurry lkg was taken up to a 3 L beaker, and 426 g of ammonium sulfate was added. Next, the mixture was mixed at a rate of about i5 rpm, i·J, and the slurry was dried in a box dryer at 90 ° C for 24 hours in the air to obtain 760 g of a dried product. Ο The dried product is heated in a small electric furnace at 50 (TC, 6 hours, and heated to obtain 520 g of rare earth sulfate.) The fluorine gas and ammonia gas generated at this time are absorbed into the aqueous solution to form ammonium fluoride. In the aqueous solution, ammonia is recovered in the step (7) described later, and the fluorine component is recovered and discarded in the form of calcium fluoride. The rare earth sulfate is dissolved in 20 L of water to obtain a rare earth elemental solution. (Separating from the acidic solution (slurry) of the rare earth element, the undissolved residue containing Si, A, Fe, the step (2)), and the acidic solution (slurry) in the mixture, at 120 rpm Under the conditions, an ammonium hydrogencarbonate solution having a concentration of 1% by weight as a pH adjuster is added, and the mixture is adjusted to pH 5.5 and stirred for an hour. At this time, the carbonation gas system formed by the neutralization reaction is dispersed with water vapor. / The liquid mixture is in a boiling state in appearance. Therefore, the liquid is cooled by a reflux condenser to condense water. After the gas is condensed, the carbon dioxide gas absorption device of the step (8) described later is introduced to carry out the reaction absorption by 097137448 24 200925112 ammonia. money Next, a Nutsche-type suction vessel having an inner diameter of 300 mm φ is used, and a filter paper (AdvanteCh manufactured by Toyo Co., Ltd.) is used to separate solid and liquid undissolved components into solids without the need to reduce the amount of miscellaneously solved the recovery of the rare earth element-based mechanically mixed aqueous solution. The quality of the dry product based on the solid content (rejection required) is 75g. 'Analysis by the fluorescent X-ray method confirms that the composition is ❹ dioxide, dream, iron. (3) (from rare earths The solution causes rare earth carbonate to be formed and crystallized: step (3)) The acidic aqueous solution in which the filtered rare earth element is dissolved is heated to about 6 (rc) under stirring conditions of 12 (four) m. Secondly, about 2 逐 is added successively. The mass % concentration of the acid-destroying hydrogen recorded solution is 2 〇〇〇g, and the reaction of the following formula (1) is successively performed to generate crystals of the rare earth carbonate and crystallize.
Ln2(S〇4)3 + 6HN4HC〇3-^Ln2(C〇3)3 | + 3(NH4)2S〇4+3C〇2 f + φ 3H2〇 (1) (式(1)中’ Ln表示稀土類元素。) 所添加之碳酸氫銨,係如上式所示般,與硫酸稀土進行反 .應而生成碳酸稀土,並釋出碳酸氣體。碳酸氫銨添加後約 30分鐘時,碳酸氣體之產生停止,可確認到反應之結束, 故冷邠至40C並停止攪拌。又,於反應中副產生之碳酸氣 體係以反應器上部之迴流冷凝器進行冷卻後,導入至步驟(8) 之碳酸氣體吸收裝置中,並與氨進行反應(碳酸化反應),而 097137448 25 200925112 回收為碳酸氫銨。 (4)(碳酸稀土之分離,步驟(4)) 將上述含有碳酸稀土之漿料,以内徑300mmφ之Nutseh 式吸引過濾器並使用No. 5A濾紙(Advantech東洋公司製)進 行過濾、,於滤別後以500g純水進行3次洗淨並回收,以* - 型乾燥機於空氣中90°C之溫度條件下進行乾燥一日夜,得 • 到320g之碳酸稀土之乾燥濾餅。 ❹ (5)(碳酸稀土之煅燒,步驟(5)) 將所得之碳酸稀土於小型電爐中,以500°C進行煅燒5小 時,回收稀土類氧化物235g。自廢研磨劑漿料之以氧化稀 土成分換算計的回收率為約95%。 另外,此時所產生之碳酸氣體係導入至步驟(8)中之碳酸 氣體吸收裝置中,使其與氨反應(碳酸化反應)而回收為碳酸 氫銨。 © (6)(硫酸錄及水之回收,步驟(6)) 於步驟(4)中,將自碳酸稀土漿料進行碳酸稀土之分離作 業而得之濾液(硫酸銨水溶液)約25〇〇〇g進行蒸餾濃縮(濃 縮分離)’而分離•回收硫酸銨水溶液2〇〇〇g及水23〇〇〇g。 取硫酸銨水溶液之一部分,藉蒸發乾固法所求得之固形份濃 度為14. 5質量%。 (7)(氨之回收,步驟(7)) 於步驟(1)中,於自煅燒步驟所回收之氟化銨水溶液約 097137448 26 200925112 600g中’添加屬於強鹼劑之25%氫氧化鈣溶 使氟化如搬,將其藉喊去除 ;^儿版劑’ 液約80〇ff。η 液之型式回收氨水溶 辰_g。回收液中之氨濃度為約6.0質量%。 另外,針對溶液中所含之氟成分 吐徒其忐法 力J添加虱氧化鈣,藉 、成為不溶性之氟化鈣而無害化處理, 回收。苴可褙愿過冼淨予以 分。,、了知廢棄,但亦可再次添加作為研磨劑中之氣成 〇 ⑻(碳酸氣體之回收及碳酸紐之合成,步驟⑻) =⑻之魏化反應’如圖2所讀,以具備碳酸氣 體導入匈導人糾、齡他、溫賴料段3、冷凝 器4、逆流接觸式吸收塔5 _拌式吸收裝置(附冷凝器之 攪拌槽)R(内徑φ12〇_χ槽高hl5Q_,附有紫式擾拌翼⑽ x60W))進行實施。亦即’於該附有冷凝器之鮮槽r中,填 裝上述所回收之6.0質量%之氨讀液之總量與反應吸收用 © 氨水6。 將其以150學之速度進行搜拌,並於外部被套3使冷水 流動而將内溫·冷卻至20 C,將上部冷凝器4冷卻至1〇。〇。 其次,藉該攪拌槽之碳酸氣體導入管丨,使碳酸氣體(於 酸性稀土類溶液中,添加碳酸氫錢而使碳酸稀土生成時所發 生之反應生成氣體)於吸收用氨水6進行汽提,使碳酸氣體 被反應吸收,而生成碳酸氮錢。 採取藉反應吸收所生成之回收碳酸氫銨漿料之一部分,藉 097137448 27 200925112 蒸發乾固法所求得之固形份濃度為28質量%,由此所計算之 碳醆氫銨之生成量為224g。 其意味著於硫酸銨中之約87%之氨以碳酸氫銨之型式被 回收,視需要,可於該水溶液中追加新鮮之碳酸氫敍或水 刀直接予以回收至碳酸稀土生成•晶析步驟中並再利用作 為碳酸稀土合成(步驟(3))之原料。 -將以步驟(5)所回收之稀土類氧化物及新品之稀土類氧化 ❹物之以icp發光分析法(島津製作所製,ShimadzuLn2(S〇4)3 + 6HN4HC〇3-^Ln2(C〇3)3 | + 3(NH4)2S〇4+3C〇2 f + φ 3H2〇(1) (in the formula (1), 'Ln The rare earth element.) The ammonium hydrogencarbonate added is reversed with a rare earth sulfate as shown in the above formula to form a rare earth carbonate and release a carbonic acid gas. About 30 minutes after the addition of ammonium hydrogencarbonate, the generation of carbonic acid gas was stopped, and the end of the reaction was confirmed, so that the mixture was cooled to 40 C and stirring was stopped. Further, the carbon dioxide gas system which is produced by the reaction in the reaction is cooled by a reflux condenser in the upper portion of the reactor, and then introduced into the carbonic acid gas absorption device of the step (8), and reacted with ammonia (carbonation reaction), and 097137448 25 200925112 Recovered as ammonium bicarbonate. (4) (Separation of rare earth carbonate, step (4)) The above-mentioned slurry containing rare earth carbonate is filtered by a Nutseh-type suction filter having an inner diameter of 300 mmφ, and filtered using No. 5A filter paper (manufactured by Advantech Toyo Co., Ltd.). After that, it was washed and recovered three times with 500 g of pure water, and dried in a *-type dryer at 90 ° C in the air overnight to obtain a dry filter cake of 320 g of rare earth carbonate. (5) (Calculation of rare earth carbonate, step (5)) The obtained rare earth carbonate was calcined at 500 ° C for 5 hours in a small electric furnace to recover 235 g of a rare earth oxide. The recovery rate of the waste abrasive slurry in terms of oxidized rare earth component was about 95%. Further, the carbon dioxide gas system produced at this time is introduced into the carbon dioxide gas absorption apparatus in the step (8), and reacted with ammonia (carbonation reaction) to recover ammonium hydrogencarbonate. © (6) (Recovery of Sulfuric Acid Recording Water, Step (6)) In the step (4), the filtrate (ammonium sulfate aqueous solution) obtained by separating the rare earth carbonate slurry from the rare earth carbonate slurry is about 25 〇〇〇. g is subjected to distillation concentration (concentration separation) to separate and recover 2 g of aqueous ammonium sulfate solution and 23 g of water. 5质量质量。 The solid part of the aqueous solution was determined to be 1. 5 mass%. (7) (Ammonia recovery, step (7)) In the step (1), in the ammonium fluoride aqueous solution recovered from the calcination step, about 097137448 26 200925112 600g 'add 25% calcium hydroxide dissolved in a strong alkali agent To make the fluorination move, remove it by shouting; ^ pediatric agent 'liquid about 80 〇 ff. The type of η liquid recovers ammonia water _g. The ammonia concentration in the recovered liquid was about 6.0% by mass. In addition, calcium sulphate is added to the fluorine component contained in the solution, and calcium sulphate is added to the insoluble calcium fluoride to be harmlessly treated and recovered. I wish I would rather share it. , knowing to discard, but can also be added as a gas in the abrasive 〇 (8) (recovery of carbonic acid gas and synthesis of carbonic acid, step (8)) = (8) Weihua reaction 'as read in Figure 2, to have carbonic acid The gas is introduced into the Hungarian guide, the age, the temperature, the temperature, the third, the condenser 4, the countercurrent contact absorption tower 5 _ the mixing absorption device (with the condenser agitation tank) R (inner diameter φ12 〇 χ 高 high hl5Q_ It is carried out with a purple-type scrambled wing (10) x60W)). That is, the total amount of the 6.0% by mass of the ammonia reading liquid recovered and the reaction absorption © ammonia water 6 were filled in the fresh tank r with the condenser. This was mixed at a rate of 150 liters, and the outer jacket 3 was allowed to flow cold water to cool the inner temperature to 20 C, and the upper condenser 4 was cooled to 1 Torr. Hey. Then, the carbon dioxide gas is introduced into the tube by the agitation tank, and the carbon dioxide gas (the reaction gas generated when the rare earth carbonate is formed by adding hydrogen carbonate to the acidic rare earth solution) is stripped in the ammonia water for absorption 6 . The carbonic acid gas is absorbed by the reaction to form a carbonic acid nitrogen coin. Taking a part of the recovered ammonium bicarbonate slurry generated by the reaction absorption, the solid content obtained by the evaporation dry solid method by 097137448 27 200925112 is 28% by mass, and the calculated amount of the carbonium hydrogen ammonium hydroxide calculated is 224 g. . It means that about 87% of the ammonia in the ammonium sulfate is recovered in the form of ammonium hydrogencarbonate, and if necessary, fresh hydrogen carbonate or water jet can be added to the aqueous solution to directly recover the rare earth carbonate formation and crystallization step. It is reused as a raw material for the synthesis of rare earth carbonate (step (3)). - icp luminescence analysis method of rare earth oxides obtained by the step (5) and rare earth oxides of the new product (Shimadzu, Shimadzu Corporation)
Corporation)所得的分析值示於表2。由表明顯可知,使於 研磨及研磨劑漿料濃縮步驟中所混入之微量雜質成分(微量 汙染物,Trace Contaminant)的二氧化矽、氧化鋁、鐵成分 去除99%以上,於純度方面毫不遜色於工業性取得者。 (表2) (稀土類氧化物之組成) 成分 TRE0~~1 Si〇2 〜 AI2O3 Fe2〇3 —含量(皙晉幻 一 _____廢研磨劑漿料 新品 回收品— — 78.4 91.2 90.4 3. 6 ] <0. 03 <0. 03 — 1.0 6.9 —' <0. 03 Γ <0.03 <0. 03 <〇. 〇3 F ---—J — 5.2 <0. 01 <0. 01 ❹ 氧化物作為補,於既定條件下進行粉碎,同_經粉碎處 理調整之氟化稀土依既定條件進行調合、混合、緞燒、粉碎、 097137448 28 200925112 分級、而作成岍 度),使用_AI 其進行㈣化處理(約10質量%濃 果示於表3 產業公司製阽型研磨器評價研磨特性,結 (表3) (回收氧化稀土之μ —一~磨特性) 使用新品原- 相對研磨速度 (損傷、平坦度)- 1.0 〇 Γ~7~^一-原料 由矣3 B日舶, 1.0 〇 一 〇 ^ n尺災用丨所回收之原料的研磨劑, β a】與使用了新品原料之研磨劑同等的研磨速度、表面 狀態。 [實施例2] 、除了將下述之外,其餘依與實施例1相同之方 法回收稀土類元素之氧化物:⑴將步驟⑴所使用之硫酸 銨,為實施例1所回收之硫酸銨水溶液2〇〇〇g及於其追加了 試藥之硫酸銨150g者;(U)用於溶解硫酸稀土之水,為實 施例1所回收之水20L ;及(iii)步驟(4)所使用之碳酸氫 銨,為於實施例1所回收之碳酸氫銨水溶液8〇〇g中,追加 了試藥之碳酸氫銨180g者。 將所回收之稀土類氧化物及新品之稀土類氧化物之以 ICP發光分析法(島津製作所製)所得的分析值示於表4。由 表明顯可知,使於研磨及研磨劑漿料濃縮步驟中所混入之微 097137448 29 200925112 量雜質成分的二氧化矽、氧化鋁、鐵成分去除99%以上’於 純度方面毫不遜色於工業性取得者。 (表4) (稀土類氧化物之組成) 成分 含量(質量%) __ 廢研磨劑漿 料 新品 回收品 ______—1 TRE0 ------- 78.4 91. 2 Si〇2 3.6 <0.03 Al2〇3 1.0 <0· 03 Fe2〇a - 6. 9 Γ <〇.〇3 F 5.2 <0.01 <AJi— _ II _ — 將經回收之稀土類元素之氧化物及新品之稀土類元素之 氧化物作為原料,於既定條件下進行粉碎,同時與經粉碎處 理調整之氟化稀土依既定條件進行調合、混合、煅燒、粉碎、 分級而作成研磨劑。對其進行漿料化處理(約10質量%濃 度)使用HAMAI產業公司製⑽型研磨器評價研磨特性,結 〇 果示於表5。 (表5) 土之研磨特性) ----- 相對研磨速度 外觀 (損傷 1.0 _- 原料 To Ο__ =了传到與使用了新品原料之研磨劑同等的研磨速度、表面 由表5明顯 狀態。 097137448 30 200925112 (產業上之可利用性) 根據本發明,提供一種廉價製程,係自研磨速度大幅降低 而通常被廢棄之含有稀土類元素的廢研磨劑漿料’效率佳地 回收尚品質之稀土類氧化物,並可將其再次使用作為具有尚 研磨速度之研磨劑。 另外,根據本發明,由於可將自製程中所排出之氨氣體、 碳酸氣體、硫酸銨及水全部回收再利用,故不僅是稀土類元 ❹ 素,該製程中之使用藥劑亦可回收,而提供半永久性之回收 製程。 尤其是用於碳酸稀土之生成•晶析的碳酸氫銨,由於係藉 由自製程中所排出之氨氣體及碳酸氣體的碳酸化反應而回 收再利用碳酸氫銨,故可回收使用高價之碳酸氩銨。 另外’用於生成硫酸稀土之硫酸銨,係自於碳酸稀土之生 成·晶析時之含有碳酸稀土之漿料的濾液進行回收’並可再 ❹ 次使用作為硫酸稀土生成之反應藥劑,故步驟廢液之無害化 處理變得簡易。 再者’根據本發明,預先將硫酸稀土水溶液調整為特定之 ' PH並進行固液分離,藉此可選擇性地使溶解共存之鐵離子 等雜質沉澱去除,而可容易製造、回收高純度之碳酸稀土類。 如以上所述,本發明於產業上之可利用性極大。 【圖式簡單說明】 圖1為顯示本發明之包括碳酸氫錢之回收步驟、硫酸錢及 097137448 31 200925112 水之回收步驟的稀土類元素之回收步驟的流程圖 (flow-sheet) ° 圖2為顯示使碳酸氣體以氨水進行反應吸收而形成碳酸 氫銨的反應容器的說明圖。 【主要元件符號說明】The analytical values obtained by Corporation) are shown in Table 2. It is apparent from the table that the cerium oxide, aluminum oxide and iron components of the trace impurity component (Trace Contaminant) mixed in the polishing and polishing slurry concentration step are removed by 99% or more, and the purity is not Inferior to industrial gainers. (Table 2) (Composition of rare earth oxides) Component TRE0~~1 Si〇2~ AI2O3 Fe2〇3—Content (皙晋幻一_____ Waste abrasive slurry new product recovery – 78.4 91.2 90.4 3. 6 ] <0. 03 <0. 03 — 1.0 6.9 —' <0. 03 Γ <0.03 <0. 03 <〇. 〇3 F ---—J — 5.2 <0. 01 <0. 01 ❹ Oxide as a supplement, pulverized under the established conditions, and the fluorinated rare earth adjusted by the pulverization treatment is blended, mixed, satin-fired, pulverized, 097137448 28 200925112, and the enthalpy is formed according to the predetermined conditions. ), using _AI to carry out (four) treatment (about 10% by mass of concentrated fruit is shown in Table 3). The grinding characteristics of the 研磨 type grinder are evaluated by the industrial company, and the knot (Table 3) (recovering the oxidized rare earth μ-one-grinding property) is used. New product original - Relative grinding speed (damage, flatness) - 1.0 〇Γ~7~^一-Materials from 矣3 B Japanese ship, 1.0 〇一〇^ n 灾 Disaster used for the recovery of raw materials, β a The polishing rate and surface state are the same as those of the abrasive using the new material. [Example 2] Except for the following, 1) The oxide of the rare earth element is recovered by the same method: (1) the ammonium sulfate used in the step (1) is 2 〇〇〇g of the ammonium sulfate aqueous solution recovered in the first embodiment, and 150 g of the ammonium sulfate to which the reagent is added; (U) water for dissolving rare earth sulfate, 20 L of water recovered in Example 1, and (iii) ammonium hydrogencarbonate used in the step (4), which is an aqueous solution of ammonium hydrogencarbonate recovered in Example 1. In the 〇g, the amount of the ammonium hydrogencarbonate to be added was 180 g. The analysis values obtained by the ICP emission spectrometry (manufactured by Shimadzu Corporation) of the rare earth oxides and the rare earth oxides of the new products are shown in Table 4. It is apparent from the table that the cerium oxide, aluminum oxide and iron components of the impurity component of the micro-097137448 29 200925112 mixed in the polishing and polishing slurry concentration step are removed by 99% or more in terms of purity. (Table 4) (Composition of rare earth oxides) Component content (% by mass) __ Waste abrasive slurry new product recovery ______—1 TRE0 ------- 78.4 91. 2 Si〇2 3.6 <0.03 Al2〇3 1.0 <0· 03 Fe2〇a - 6. 9 Γ <〇.〇3 F 5.2 <0.01 <AJi- _ II _ — The oxide of the rare earth element recovered and the rare earth element of the new product are used as raw materials, and are pulverized under the predetermined conditions. At the same time, the fluorinated rare earth adjusted by the pulverization treatment is blended, mixed, calcined, pulverized, and classified according to the predetermined conditions to form an abrasive. The slurrying property (about 10% by mass) was evaluated by using a grinder (10) manufactured by HAMAI Industries Co., Ltd., and the results are shown in Table 5. (Table 5) Grinding characteristics of soil) ----- Relative polishing speed appearance (damage 1.0 _- Raw material To Ο__ = The same grinding speed as that of the abrasive using new raw materials, and the surface is apparent from Table 5. 097137448 30 200925112 (Industrial Applicability) According to the present invention, there is provided an inexpensive process which is a rare earth element-containing waste abrasive slurry which is generally discarded since the polishing rate is greatly reduced. An oxide-like oxide can be reused as an abrasive having a polishing rate. Further, according to the present invention, since ammonia gas, carbonic acid gas, ammonium sulfate, and water discharged from the self-made process can be completely recovered and reused, It is not only a rare earth element, but also a semi-permanent recycling process for the use of chemicals in the process, especially for the formation and crystallization of rare earth carbonates, due to the self-made process. The carbonation reaction of the discharged ammonia gas and the carbonic acid gas recovers and reuses ammonium hydrogencarbonate, so that high-priced ammonium argon carbonate can be recovered and used. The ammonium sulfate of rare earth sulfate is recovered from the filtrate containing the rare earth carbonate slurry during the formation and crystallization of rare earth carbonate, and can be reused as a reaction agent for generating rare earth sulfate, so that the waste liquid of the step is harmless. Further, according to the present invention, the rare earth sulfate aqueous solution is previously adjusted to a specific 'PH' and subjected to solid-liquid separation, whereby impurities such as dissolved iron ions can be selectively precipitated and removed, and can be easily produced. The high-purity rare earth carbonate is recovered. As described above, the present invention has great industrial applicability. [Simplified Schematic] FIG. 1 is a diagram showing the recovery step of the present invention including hydrogen carbonate money, sulfuric acid money and 097137448 31 200925112 Flow-sheet of the step of recovering the rare earth element in the water recovery step. Fig. 2 is an explanatory view showing a reaction vessel for reacting carbonic acid gas with ammonia water to form ammonium hydrogencarbonate. Description]
1 喷嘴(碳酸氣體導入手段) 2 攪拌手段 3 冷卻被套(溫度調節手段) 4 冷凝器 5 逆流接觸式吸收塔 6 反應吸收用氨水 9 研磨步驟 10 廢研磨劑漿料 20 硫酸錢 20c 經濃縮分離之回收硫酸銨 30 混合步驟 33 乾燥步驟 35 焙燒步驟 40 硫酸稀土 43 溶解用水 43c 經濃縮分離之回收水 45 溶解步驟 50 pH調節劑 097137448 32 2009251121 Nozzle (carbonic acid gas introduction means) 2 Stirring means 3 Cooling jacket (temperature adjustment means) 4 Condenser 5 Countercurrent contact absorption tower 6 Reaction absorption ammonia water 9 Grinding step 10 Waste abrasive slurry 20 Sulfuric acid money 20c Separated and separated Recovery of ammonium sulfate 30 Mixing step 33 Drying step 35 Calcination step 40 Rare earth sulfate 43 Dissolved water 43c Concentrated separated recovered water 45 Dissolving step 50 pH adjusting agent 097137448 32 200925112
53 60 63 65 70 73 80 83 85 87 89 90 93 100 105 110 112 115 117 119 120 130 pH調節步驟 固液分離步驟 殘渣(固體不需成分) 廢棄步驟 溶解了稀土類元素(氧化稀土)之酸性水溶液 碳酸氫銨 碳酸稀土生成•晶析步驟 含有碳酸稀土之衆料 碳酸氣體 固液分離步驟 碳酸烯土 滤液 濃縮分離步驟 煅燒步驟 氧化稀土 沉殿劑(氫氧化鈣等) 廢氣吸收步驟 過濾步驟 殘渣 廢棄步驟 氨水 碳酸化反應步驟 097137448 3353 60 63 65 70 73 80 83 85 87 89 90 93 100 105 110 112 115 117 119 120 130 pH adjustment step Solid-liquid separation step residue (solids do not require components) The waste step dissolves the acidic aqueous solution of rare earth elements (rare earth oxide) Ammonium bicarbonate carbonate rare earth formation • Crystallization step containing rare earth carbonates, carbonic acid gas, solid-liquid separation step, carbonated olefin filtrate, separation and separation step, calcination step, oxidation of rare earth sinking agent (calcium hydroxide, etc.), exhaust gas absorption step, filtration step, residue disposal step Ammonia water carbonation reaction step 097137448 33
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| JP2007259735A JP5086021B2 (en) | 2007-10-03 | 2007-10-03 | Recovery method of rare earth elements |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN104185606A (en) * | 2011-12-07 | 2014-12-03 | 齐龙工业陶瓷公司 | Method for recycling rare earth and zirconia materials |
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| WO2013099666A1 (en) | 2011-12-27 | 2013-07-04 | コニカミノルタ株式会社 | Method for separating polishing material and regenerated polishing material |
| US20160068929A1 (en) * | 2014-09-08 | 2016-03-10 | Patrick R. Taylor | EXTRACTION OF RARE EARTH METALS FROM NdFeB USING SELECTIVE SULFATION ROASTING |
| CN108728642B (en) * | 2018-06-28 | 2021-03-30 | 武汉工程大学 | Method for recycling rare earth by reusing mother liquor after rare earth is precipitated by weathering crust leaching solution ammonium bicarbonate |
| CN112725623B (en) * | 2020-12-02 | 2022-09-09 | 北京工业大学 | A method for separating and extracting rare earth and regenerating rare earth polishing powder from waste rare earth polishing powder |
| CN112724839B (en) * | 2021-01-21 | 2022-03-22 | 包头华明高纳稀土新材料有限公司 | System and method for preparing rare earth polishing powder |
| CN117660787B (en) * | 2022-08-31 | 2026-05-05 | 厦门稀土材料研究所 | A method for recovering thorium and rare earth elements from rare earth waste. |
| CN115646394B (en) * | 2022-12-10 | 2025-12-19 | 包头市新源稀土高新材料有限公司 | Rare earth carbonate production system and production method |
| CN115927884A (en) * | 2022-12-30 | 2023-04-07 | 中稀(广西)金源稀土新材料有限公司 | Defluorination method for rare earth ore leaching solution |
| CN116622989A (en) * | 2023-05-18 | 2023-08-22 | 内蒙古科技大学 | A kind of removal method of phosphorus in sulfuric acid rare earth solution |
| CN117127033B (en) * | 2023-08-29 | 2024-01-23 | 江苏南方永磁科技有限公司 | Rare earth metal waste residue dissolving and recycling device |
| FR3162743A1 (en) * | 2024-06-03 | 2025-12-05 | Snf Sa | METHOD FOR SEPARING RARE EARTHS IN AQUEOUS SOLUTION MIXTURE |
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| JPS5554532A (en) * | 1978-10-17 | 1980-04-21 | Mitsui Mining & Smelting Co Ltd | Ammonia recovering method |
| JPS5913625A (en) * | 1982-07-09 | 1984-01-24 | Asahi Chem Ind Co Ltd | Manufacture of oxysulfide of rare earth element |
| JPH06254764A (en) * | 1993-03-03 | 1994-09-13 | Asahi Glass Co Ltd | Regenerating method for polishing liquid |
| JPH10237562A (en) * | 1997-02-20 | 1998-09-08 | Taiyo Koukou Kk | Recovery of vanadium |
| DE19812262A1 (en) * | 1998-03-20 | 1999-09-23 | Bayer Ag | Production of gypsum and iron oxide pigments from dilute acid formed in the manufacture of titanium dioxide |
| JP2003238943A (en) * | 2002-02-18 | 2003-08-27 | Fujimi Inc | Methods for producing cerium-based abrasive and cerium oxide contained therein |
| JP4248937B2 (en) * | 2002-06-07 | 2009-04-02 | 昭和電工株式会社 | Method for recovering rare earth oxide from waste liquid containing rare earth element |
| JP4322008B2 (en) * | 2002-12-26 | 2009-08-26 | ステラケミファ株式会社 | Method for recovering tantalum compound and / or niobium compound |
| JP4982692B2 (en) * | 2006-03-17 | 2012-07-25 | Dowaエレクトロニクス株式会社 | Catalyst cerium oxide powder and DPF |
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| CN104185606A (en) * | 2011-12-07 | 2014-12-03 | 齐龙工业陶瓷公司 | Method for recycling rare earth and zirconia materials |
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| JP2009083082A (en) | 2009-04-23 |
| TWI387559B (en) | 2013-03-01 |
| JP5086021B2 (en) | 2012-11-28 |
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