CN109108049A - Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag - Google Patents
Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag Download PDFInfo
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- CN109108049A CN109108049A CN201810867455.1A CN201810867455A CN109108049A CN 109108049 A CN109108049 A CN 109108049A CN 201810867455 A CN201810867455 A CN 201810867455A CN 109108049 A CN109108049 A CN 109108049A
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- dangerous waste
- conversion
- slag
- mill
- fluorochemical
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- 239000002699 waste material Substances 0.000 title claims abstract description 114
- 239000002893 slag Substances 0.000 title claims abstract description 92
- 229910052782 aluminium Inorganic materials 0.000 title claims abstract description 85
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 title claims abstract description 75
- 239000004411 aluminium Substances 0.000 title claims abstract description 62
- 239000011734 sodium Substances 0.000 title claims abstract description 56
- 229910052708 sodium Inorganic materials 0.000 title claims abstract description 44
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 title claims abstract description 43
- 238000000034 method Methods 0.000 title claims abstract description 43
- 230000009466 transformation Effects 0.000 title claims abstract description 20
- 238000006243 chemical reaction Methods 0.000 claims abstract description 88
- 239000007788 liquid Substances 0.000 claims abstract description 26
- 229910052731 fluorine Inorganic materials 0.000 claims abstract description 25
- 239000011737 fluorine Substances 0.000 claims abstract description 25
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims abstract description 22
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 21
- 238000012545 processing Methods 0.000 claims abstract description 21
- 230000008569 process Effects 0.000 claims abstract description 19
- 230000001131 transforming effect Effects 0.000 claims abstract description 18
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 claims abstract description 17
- 238000003801 milling Methods 0.000 claims abstract description 17
- 229910052500 inorganic mineral Inorganic materials 0.000 claims abstract description 16
- 239000011707 mineral Substances 0.000 claims abstract description 16
- 238000010438 heat treatment Methods 0.000 claims abstract description 15
- JMANVNJQNLATNU-UHFFFAOYSA-N glycolonitrile Natural products N#CC#N JMANVNJQNLATNU-UHFFFAOYSA-N 0.000 claims abstract description 13
- 150000001875 compounds Chemical class 0.000 claims abstract description 11
- -1 cyanogen compound Chemical class 0.000 claims abstract description 9
- 238000001035 drying Methods 0.000 claims abstract description 7
- MTHSVFCYNBDYFN-UHFFFAOYSA-N diethylene glycol Chemical compound OCCOCCO MTHSVFCYNBDYFN-UHFFFAOYSA-N 0.000 claims description 36
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 32
- 229910052799 carbon Inorganic materials 0.000 claims description 31
- 239000000463 material Substances 0.000 claims description 27
- 239000007789 gas Substances 0.000 claims description 26
- 239000000203 mixture Substances 0.000 claims description 23
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 21
- 238000004458 analytical method Methods 0.000 claims description 20
- 239000002002 slurry Substances 0.000 claims description 20
- 238000003860 storage Methods 0.000 claims description 17
- 239000000126 substance Substances 0.000 claims description 14
- 239000011812 mixed powder Substances 0.000 claims description 13
- 239000007787 solid Substances 0.000 claims description 13
- KLZUFWVZNOTSEM-UHFFFAOYSA-K Aluminium flouride Chemical compound F[Al](F)F KLZUFWVZNOTSEM-UHFFFAOYSA-K 0.000 claims description 12
- 238000010521 absorption reaction Methods 0.000 claims description 11
- 230000003647 oxidation Effects 0.000 claims description 11
- 238000007254 oxidation reaction Methods 0.000 claims description 11
- 238000000926 separation method Methods 0.000 claims description 10
- 239000000243 solution Substances 0.000 claims description 10
- 230000015572 biosynthetic process Effects 0.000 claims description 9
- 238000002425 crystallisation Methods 0.000 claims description 9
- 230000008025 crystallization Effects 0.000 claims description 9
- 238000000227 grinding Methods 0.000 claims description 8
- 150000002500 ions Chemical class 0.000 claims description 8
- 239000002245 particle Substances 0.000 claims description 8
- 229910001634 calcium fluoride Inorganic materials 0.000 claims description 7
- 229910001635 magnesium fluoride Inorganic materials 0.000 claims description 7
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims description 6
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims description 6
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 6
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 claims description 6
- 229910052791 calcium Inorganic materials 0.000 claims description 6
- WUKWITHWXAAZEY-UHFFFAOYSA-L calcium difluoride Chemical compound [F-].[F-].[Ca+2] WUKWITHWXAAZEY-UHFFFAOYSA-L 0.000 claims description 6
- 239000000292 calcium oxide Substances 0.000 claims description 6
- 238000001514 detection method Methods 0.000 claims description 6
- 230000008676 import Effects 0.000 claims description 6
- 239000000843 powder Substances 0.000 claims description 6
- 238000005406 washing Methods 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 5
- 229910052593 corundum Inorganic materials 0.000 claims description 5
- 229910001610 cryolite Inorganic materials 0.000 claims description 5
- 229910052749 magnesium Inorganic materials 0.000 claims description 5
- 229910052760 oxygen Inorganic materials 0.000 claims description 5
- 238000012216 screening Methods 0.000 claims description 5
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 claims description 4
- 239000012141 concentrate Substances 0.000 claims description 4
- 238000006073 displacement reaction Methods 0.000 claims description 4
- 239000003292 glue Substances 0.000 claims description 4
- QIQXTHQIDYTFRH-UHFFFAOYSA-N octadecanoic acid Chemical compound CCCCCCCCCCCCCCCCCC(O)=O QIQXTHQIDYTFRH-UHFFFAOYSA-N 0.000 claims description 4
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 claims description 4
- 150000005846 sugar alcohols Polymers 0.000 claims description 4
- 229910002567 K2S2O8 Inorganic materials 0.000 claims description 3
- 229910004882 Na2S2O8 Inorganic materials 0.000 claims description 3
- 229910000831 Steel Inorganic materials 0.000 claims description 3
- 238000005275 alloying Methods 0.000 claims description 3
- 239000010431 corundum Substances 0.000 claims description 3
- 238000001704 evaporation Methods 0.000 claims description 3
- 230000008020 evaporation Effects 0.000 claims description 3
- 125000001153 fluoro group Chemical group F* 0.000 claims description 3
- 238000000265 homogenisation Methods 0.000 claims description 3
- 238000007689 inspection Methods 0.000 claims description 3
- 239000011344 liquid material Substances 0.000 claims description 3
- 229910052744 lithium Inorganic materials 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 239000008188 pellet Substances 0.000 claims description 3
- 229910052573 porcelain Inorganic materials 0.000 claims description 3
- 229910052700 potassium Inorganic materials 0.000 claims description 3
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 3
- MNWBNISUBARLIT-UHFFFAOYSA-N sodium cyanide Chemical compound [Na+].N#[C-] MNWBNISUBARLIT-UHFFFAOYSA-N 0.000 claims description 3
- 239000007790 solid phase Substances 0.000 claims description 3
- 238000001179 sorption measurement Methods 0.000 claims description 3
- 239000010935 stainless steel Substances 0.000 claims description 3
- 229910001220 stainless steel Inorganic materials 0.000 claims description 3
- 239000010959 steel Substances 0.000 claims description 3
- WRIDQFICGBMAFQ-UHFFFAOYSA-N (E)-8-Octadecenoic acid Natural products CCCCCCCCCC=CCCCCCCC(O)=O WRIDQFICGBMAFQ-UHFFFAOYSA-N 0.000 claims description 2
- LQJBNNIYVWPHFW-UHFFFAOYSA-N 20:1omega9c fatty acid Natural products CCCCCCCCCCC=CCCCCCCCC(O)=O LQJBNNIYVWPHFW-UHFFFAOYSA-N 0.000 claims description 2
- QSBYPNXLFMSGKH-UHFFFAOYSA-N 9-Heptadecensaeure Natural products CCCCCCCC=CCCCCCCCC(O)=O QSBYPNXLFMSGKH-UHFFFAOYSA-N 0.000 claims description 2
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 claims description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims description 2
- KRKNYBCHXYNGOX-UHFFFAOYSA-K Citrate Chemical compound [O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O KRKNYBCHXYNGOX-UHFFFAOYSA-K 0.000 claims description 2
- 229910002651 NO3 Inorganic materials 0.000 claims description 2
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims description 2
- 239000005642 Oleic acid Substances 0.000 claims description 2
- ZQPPMHVWECSIRJ-UHFFFAOYSA-N Oleic acid Natural products CCCCCCCCC=CCCCCCCCC(O)=O ZQPPMHVWECSIRJ-UHFFFAOYSA-N 0.000 claims description 2
- 235000021355 Stearic acid Nutrition 0.000 claims description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims description 2
- GSEJCLTVZPLZKY-UHFFFAOYSA-N Triethanolamine Chemical compound OCCN(CCO)CCO GSEJCLTVZPLZKY-UHFFFAOYSA-N 0.000 claims description 2
- SLINHMUFWFWBMU-UHFFFAOYSA-N Triisopropanolamine Chemical compound CC(O)CN(CC(C)O)CC(C)O SLINHMUFWFWBMU-UHFFFAOYSA-N 0.000 claims description 2
- 150000001408 amides Chemical class 0.000 claims description 2
- 150000001412 amines Chemical class 0.000 claims description 2
- 229910001870 ammonium persulfate Inorganic materials 0.000 claims description 2
- 239000007864 aqueous solution Substances 0.000 claims description 2
- 239000000460 chlorine Substances 0.000 claims description 2
- 229910052801 chlorine Inorganic materials 0.000 claims description 2
- 239000003818 cinder Substances 0.000 claims description 2
- 239000003599 detergent Substances 0.000 claims description 2
- 238000001914 filtration Methods 0.000 claims description 2
- 235000011187 glycerol Nutrition 0.000 claims description 2
- QXJSBBXBKPUZAA-UHFFFAOYSA-N isooleic acid Natural products CCCCCCCC=CCCCCCCCCC(O)=O QXJSBBXBKPUZAA-UHFFFAOYSA-N 0.000 claims description 2
- 239000011259 mixed solution Substances 0.000 claims description 2
- OQCDKBAXFALNLD-UHFFFAOYSA-N octadecanoic acid Natural products CCCCCCCC(C)CCCCCCCCC(O)=O OQCDKBAXFALNLD-UHFFFAOYSA-N 0.000 claims description 2
- ZQPPMHVWECSIRJ-KTKRTIGZSA-N oleic acid Chemical compound CCCCCCCC\C=C/CCCCCCCC(O)=O ZQPPMHVWECSIRJ-KTKRTIGZSA-N 0.000 claims description 2
- 229910000027 potassium carbonate Inorganic materials 0.000 claims description 2
- 239000012286 potassium permanganate Substances 0.000 claims description 2
- 230000005070 ripening Effects 0.000 claims description 2
- 238000005070 sampling Methods 0.000 claims description 2
- GTSHREYGKSITGK-UHFFFAOYSA-N sodium ferrocyanide Chemical compound [Na+].[Na+].[Na+].[Na+].[Fe+2].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-].N#[C-] GTSHREYGKSITGK-UHFFFAOYSA-N 0.000 claims description 2
- GCLGEJMYGQKIIW-UHFFFAOYSA-H sodium hexametaphosphate Chemical compound [Na]OP1(=O)OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])OP(=O)(O[Na])O1 GCLGEJMYGQKIIW-UHFFFAOYSA-H 0.000 claims description 2
- CHQMHPLRPQMAMX-UHFFFAOYSA-L sodium persulfate Chemical compound [Na+].[Na+].[O-]S(=O)(=O)OOS([O-])(=O)=O CHQMHPLRPQMAMX-UHFFFAOYSA-L 0.000 claims description 2
- 239000008117 stearic acid Substances 0.000 claims description 2
- DNIAPMSPPWPWGF-UHFFFAOYSA-N Propylene glycol Chemical compound CC(O)CO DNIAPMSPPWPWGF-UHFFFAOYSA-N 0.000 claims 3
- 238000004519 manufacturing process Methods 0.000 abstract description 14
- KRHYYFGTRYWZRS-UHFFFAOYSA-M Fluoride anion Chemical compound [F-] KRHYYFGTRYWZRS-UHFFFAOYSA-M 0.000 abstract description 12
- 238000004064 recycling Methods 0.000 abstract description 6
- 150000002222 fluorine compounds Chemical class 0.000 abstract description 4
- 150000003388 sodium compounds Chemical class 0.000 abstract 1
- 239000000428 dust Substances 0.000 description 9
- 239000000706 filtrate Substances 0.000 description 9
- 238000002386 leaching Methods 0.000 description 9
- 239000002250 absorbent Substances 0.000 description 8
- 230000002745 absorbent Effects 0.000 description 8
- 239000003575 carbonaceous material Substances 0.000 description 8
- 239000003792 electrolyte Substances 0.000 description 8
- 239000000047 product Substances 0.000 description 8
- 239000003610 charcoal Substances 0.000 description 7
- 238000005868 electrolysis reaction Methods 0.000 description 7
- 238000005516 engineering process Methods 0.000 description 7
- 239000006096 absorbing agent Substances 0.000 description 6
- 239000012065 filter cake Substances 0.000 description 6
- 230000001698 pyrogenic effect Effects 0.000 description 6
- 239000003513 alkali Substances 0.000 description 5
- 239000011575 calcium Substances 0.000 description 5
- 238000002485 combustion reaction Methods 0.000 description 5
- 238000005188 flotation Methods 0.000 description 5
- 229910001672 fluorine mineral Inorganic materials 0.000 description 5
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 5
- 238000002156 mixing Methods 0.000 description 5
- 238000003756 stirring Methods 0.000 description 5
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 4
- 238000009833 condensation Methods 0.000 description 4
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- 239000002910 solid waste Substances 0.000 description 4
- 229910000851 Alloy steel Inorganic materials 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 238000001354 calcination Methods 0.000 description 3
- 230000008859 change Effects 0.000 description 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
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- 150000003839 salts Chemical class 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- 238000000967 suction filtration Methods 0.000 description 3
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 2
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- 229910052581 Si3N4 Inorganic materials 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical compound [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 239000001099 ammonium carbonate Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000005540 biological transmission Effects 0.000 description 2
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- 229910052681 coesite Inorganic materials 0.000 description 2
- 229910052906 cristobalite Inorganic materials 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000002001 electrolyte material Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 description 2
- 239000010881 fly ash Substances 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
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- 238000002844 melting Methods 0.000 description 2
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- 239000000377 silicon dioxide Substances 0.000 description 2
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 2
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- 229910001845 yogo sapphire Inorganic materials 0.000 description 2
- BZSXEZOLBIJVQK-UHFFFAOYSA-N 2-methylsulfonylbenzoic acid Chemical compound CS(=O)(=O)C1=CC=CC=C1C(O)=O BZSXEZOLBIJVQK-UHFFFAOYSA-N 0.000 description 1
- 229910016384 Al4C3 Inorganic materials 0.000 description 1
- USFZMSVCRYTOJT-UHFFFAOYSA-N Ammonium acetate Chemical compound N.CC(O)=O USFZMSVCRYTOJT-UHFFFAOYSA-N 0.000 description 1
- 239000005695 Ammonium acetate Substances 0.000 description 1
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- ZKQDCIXGCQPQNV-UHFFFAOYSA-N Calcium hypochlorite Chemical compound [Ca+2].Cl[O-].Cl[O-] ZKQDCIXGCQPQNV-UHFFFAOYSA-N 0.000 description 1
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- 241001269238 Data Species 0.000 description 1
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- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 1
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- 239000000378 calcium silicate Substances 0.000 description 1
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
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- 238000003682 fluorination reaction Methods 0.000 description 1
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- 230000008595 infiltration Effects 0.000 description 1
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- 229910001387 inorganic aluminate Inorganic materials 0.000 description 1
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- 229910052640 jadeite Inorganic materials 0.000 description 1
- 229910052850 kyanite Inorganic materials 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- VZCYOOQTPOCHFL-UPHRSURJSA-N maleic acid Chemical compound OC(=O)\C=C/C(O)=O VZCYOOQTPOCHFL-UPHRSURJSA-N 0.000 description 1
- 239000011976 maleic acid Substances 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 229910021527 natrosilite Inorganic materials 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 239000004584 polyacrylic acid Substances 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 125000002924 primary amino group Chemical group [H]N([H])* 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 229910052851 sillimanite Inorganic materials 0.000 description 1
- 239000001509 sodium citrate Substances 0.000 description 1
- 229910052911 sodium silicate Inorganic materials 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 239000004328 sodium tetraborate Substances 0.000 description 1
- 235000010339 sodium tetraborate Nutrition 0.000 description 1
- 239000003381 stabilizer Substances 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 229910001637 strontium fluoride Inorganic materials 0.000 description 1
- FVRNDBHWWSPNOM-UHFFFAOYSA-L strontium fluoride Chemical compound [F-].[F-].[Sr+2] FVRNDBHWWSPNOM-UHFFFAOYSA-L 0.000 description 1
- 230000001360 synchronised effect Effects 0.000 description 1
- 239000011975 tartaric acid Substances 0.000 description 1
- 235000002906 tartaric acid Nutrition 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 239000002562 thickening agent Substances 0.000 description 1
- VZCYOOQTPOCHFL-UHFFFAOYSA-N trans-butenedioic acid Natural products OC(=O)C=CC(O)=O VZCYOOQTPOCHFL-UHFFFAOYSA-N 0.000 description 1
- YWYZEGXAUVWDED-UHFFFAOYSA-N triammonium citrate Chemical compound [NH4+].[NH4+].[NH4+].[O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O YWYZEGXAUVWDED-UHFFFAOYSA-N 0.000 description 1
- BYMUNNMMXKDFEZ-UHFFFAOYSA-K trifluorolanthanum Chemical compound F[La](F)F BYMUNNMMXKDFEZ-UHFFFAOYSA-K 0.000 description 1
- 239000002912 waste gas Substances 0.000 description 1
- 229910052882 wollastonite Inorganic materials 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B2101/00—Type of solid waste
- B09B2101/02—Gases or liquids enclosed in discarded articles, e.g. aerosol cans or cooling systems of refrigerators
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B9/00—General methods of preparing halides
- C01B9/08—Fluorides
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/20—Halides
- C01F11/22—Fluorides
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F5/00—Compounds of magnesium
- C01F5/26—Magnesium halides
- C01F5/28—Fluorides
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Dispersion Chemistry (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The present invention relates in a kind of aluminium electroloysis dangerous waste slag containing sodium, the method for transformation of fluorochemical and system.Compounds containing sodium in aluminium electroloysis dangerous waste slag is transformed into not fluorine-containing soluble sodium compound including the use of transforming agent, by the mechanochemistry conversion reaction in conversion mill by method for transformation, fluorochemical is transformed into insoluble and harmless minerals fluorine compounds, cyanogen compound is oxidized and is transformed into innocuous gas, to thoroughly release the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.Conversion system includes sequentially connected dangerous waste slag crushing plant, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment is directly connected to concentration or crystallizer, drying or Equipment for Heating Processing again, and dry or Equipment for Heating Processing connects disintegrating apparatus.Present invention process is simple, be easy to be mass produced, production cost is low, three-waste free pollution, environmentally friendly, can be realized the processing target of the innoxious and recycling of aluminium electroloysis dangerous waste slag.
Description
Technical field
The present invention relates to, containing sodium, the method for transformation of fluorochemical and system, belong to electrolysis in a kind of aluminium electroloysis dangerous waste slag
Aluminum i ndustry solid waste is innoxious with application technology as the second resource field.
Background technique
It is more than 36,000,000 tons, accounts for global electricity to built about 45,000,000 tons of the aluminium electroloysis production capacity of China in 2017, actual production
Solve 50% or more of aluminium production capacity.During aluminum electrolysis, charcoal cathode due to fluorine-containing salts infiltration and expand, further cause
The breakage of electrolytic cell is scrapped.Aluminium cell generally just needs to stop groove overhaul using 4-6 or so, takes out all waste and old liner materials
Expect (referred to as slag from delining), slag from delining is inevitable solid waste during Aluminum Electrolysis Production.The every life of Aluminum Electrolysis Production
The slag from delining that 1 ton of primary aluminum about discharges 10~30kg is produced, electrolytic aluminium slag from delining is defined as danger in " National Hazard waste register "
Solid waste (classification are as follows: HW48).Slag from delining mainly accounts for about 55%, waste refractory materials by waste cathode carbon block (including thickener)
(calcium silicate board, ceramic beaverboard, insulating brick, Impervious Materials, castable, lateral mass) accounts for about 45% composition.Aluminum electrolysis waste cathode carbon
In block, carbon materials account for 30%~70%, remaining for electrolyte, mainly Na3[AlF6]、NaF、CaF2、MgF2、LiF、AlF3、
NaCN、Na4[Fe(CN)6] etc., there are also a small amount of Al, Al4C3, AlN, Na etc., these substances have soluble and react with water
Activity can generate HF, HCN, H2、CH4、NH3Deng harmful or imflammable gas, it is fluorine-containing, enter environment containing cyanogen compound can be to the mankind
And the health of animals and plants constitutes greatly harm with growth.
Aluminium electroloysis dangerous waste slag is a kind of valuable resource rich in high-graphitized carbon and fluorine-containing electrolyte.Therefore, how thorough
Bottom releases the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag, realizes the innoxious and resource utilization of aluminium electroloysis dangerous waste slag
Using being the industry difficulty for needing to capture, expert scholar and production line personnel have carried out unremitting for many years for this problem
Exploratory development.
Chinese invention CN106745137A, CN106077038A, CN106077040A, CN106745137A,
CN106587122A, CN101817521A, CN105821445A are proposed using alkali leaching or ultrasonic wave secondary flotation alkaline pressure of oxygen leaching
Method process aluminum electrolytic waste and old cathode carbon or aluminium electroloysis waste material, extract ice crystal and carbon materials respectively.Chinese invention
CN106077037A, CN106077036A, CN106180118A, CN101984984A propose auxiliary using acid processing or ultrasonic wave
Help the method process aluminum electrolytic waste and old cathode carbon or slag from delining of flotation pressurization acid processing.Chinese invention CN107162061A proposition is adopted
With alkali leaching, Ore Leaching and the united method of flyash, harmless treatment and resource are carried out to aluminum cell waste cathode carbon
Change and utilizes.
105964659 A of Chinese invention CN106064813A, CN proposition protects waste and old cathode powdered carbon at 200~400 DEG C
Temperature removes cyanogen, and except cyanogen material obtains breeze and electrolyte slag through FLOTATION SEPARATION, electrolyte slag heats at 550~800 DEG C removes charcoal
Impurity obtains electrolyte powder, and breeze goes soluble matter to obtain the powdered carbon of purity is high by alkali leaching, and alkali lixivium leads to CO2Ice crystal is precipitated
Stone and alumag.
102989744 A of Chinese invention CN, CN102989743A, CN102978659A, CN102992299A,
CN102992300A, CN102976776A are separately recovered using the method process aluminum electrolytic waste residue of water logging, flotation and high-temperature calcination
Carbon dust, refractory material.
Aluminum cell waste cathode carbon powder is soaked in water in 105772486 A of Chinese invention CN proposition, by soluble cyanogen
Compound leaches, then hydrogen peroxide, stabilizer is added (selected from citric acid, tartaric acid, ethylenediamine tetra-acetic acid, amino three in leachate
Methylene phosphonic acid, polyacrylic acid, maleic acid, borax, ammonium carbonate, ammonium hydrogen carbonate, ammonium acetate, in ammonium citrate), catalyst (choosing
From ZnO, CuO, Fe3O4、WO3In) after so that cyanide oxidation product is resolved into CO in 30~70 DEG C of reactions2、NH3Gas.Document
(China Environmental Science association Annual Conference collection of thesis in 2013: p5401~5407.) is reported using at water logging, flotation, chemistry
The research of reason, evaporative crystallization, waste gas absorption process electrolytic aluminium danger solid waste.
103239828 A of Chinese invention CN proposes a kind of program-controlled, manual electrolytic aluminium slag from delining hamlessizing technology technique,
Any one of sodium chlorate, calcium hypochlorite or hydrogen peroxide are used for except cyanogen agent, using calcium chloride, calcium oxide, calcium hydroxide or carbon
Any one of sour calcium is defluorinating agent, regulates and controls the residual quantity of pH value and fluoride in fluorine conversion process by hydrochloric acid.The patent is same
When provide the reaction warehouse and acid-regulating tank of a kind of strong acid-base resistance and strong oxidizer.
Chinese invention CN100542702C is by waste cathode of aluminum electrolytic cell carbon block and is rich in SiO2And Al2O3Flyash mixing
Carry out calcination process, treated material H2SO4With lime resolution process, obtain waste cathode of aluminum electrolytic cell carbon block innoxious
And resource utilization.Chinese invention CN107285354A by Aluminum carbonaceous dangerous waste, forge, make fluoride salt by the electricity at 1050~1200 DEG C
It is melt into liquid and is saturated separation, again low fluorine carbon granules progress high-temperature electric forged to obtain high-purity carbon product.Chinese invention
CN101054693A, CN101063215A are respectively by waste cathode of aluminum electrolytic cell powdered carbon and aluminium electrolysis anode breeze and organic binder
Mixing compacting is agglomerating, carbonaceous complete oxidation was obtained 97.5% or more electricity in calcination process 4~6 hours at 650~900 DEG C again
Solve matter product.Chinese invention CN103831285A provides a kind of including heating furnace, heat cycles devices, exhaust gas cleaner
The aluminium electroloysis breeze that gives up is carried out 7~8h of harmless treatment by processing system in 1250~1350 DEG C of heating furnace.Chinese invention
CN107628614A use 1200~1700 DEG C of temperature lower calcination electrolytic aluminium waste cathodes, by useless cathode carbon and fluorination
Object, oxide and cyanide are separated, and realize its innoxious and resource utilization.
Chinese invention CN105642649A, CN106185818A, CN106269787A use 2000 DEG C or more of superhigh temperature
With handle electrolytic aluminium waste cathode carbon block under vacuum condition, the fluoride therein of volatilizing decomposes cyanide therein, by carbon in cathode
Element, fluoride and cyanide efficiently separate decomposition, realize its innoxious and resource utilization.
From the point of view of existing technological achievement, the innoxious of aluminium electroloysis dangerous waste slag, recycling treatment are utilized and are segmented into water
The wet-treating of solution and two major class of pyrogenic attack under high temperature.Wet-treating further relate to washing (leaching), alkaline process, acid system,
Acid-alkali combination method simultaneously cooperates floatation process, and mainly for the purpose of recycling electrolyte and carbon materials, oxygen is used in wet-treating
Cyanide is resolved into harmless gaseous matter by agent.Pyrogenic attack technology is mainly negative for the purpose of innoxious, or based on giving up
Extremely middle carbonaceous content 50% or more, its calorific value resource can be effectively utilized;Or electrolyte melting permeability and separation is returned
It receives;Or HF is converted by fluoride and carries out sorption enhanced utilization again;Or it is converted into electrolyte by adding converting additive
Harmless and insoluble fluorine minerals;Or take high-temperature vacuum technology that utilization is separately recovered in carbon materials and electrolyte.?
In pyrogenic attack, it is oxidized at high temperature containing cyanogen compound and resolves into harmless gaseous matter.
From the point of view of existing technological achievement, the wet-treating and pyrogenic attack of aluminium electroloysis dangerous waste slag still have many urgent
Problem to be solved.
At least there is following main problem in current wet processing technique: the first, generated a large amount of saliferous, fluoride waste
It is not effectively addressed, causes secondary pollution;Generated H2、CH4、NH3Gas is not under control and utilizes, produced
HF cause serious pollution.The second, the electrolyte and carbon materials impurity content recycled is excessively high, cannot directly utilize.The
Three, process route is cumbersome, technology is complicated, equipment seriously corroded, and processing cost is excessively high.4th, due to aluminium electroloysis dangerous waste slag chute age
And the influence of the factors such as fluctuation of the difference of capacity, material composition, cause process parameter control difficulty big.
At least there is following main problem in current pyrogenic attack technology: the first, producing a large amount of entrainment HF and dust
Tail gas need to administer.The second, electrolytic salt recycling is not thorough, remains in carbon materials or clinker and need further to locate
Reason.Third, low melting point electrolytic salt occur vitreous clinker in furnace, cause the incomplete residual quantity of Carbon Materials oxidizing fire big,
Vitreous clinker causes production status deterioration, production stability poor in furnace.4th, reaction mass is difficult to realize the uniform of molecular level
It mixes, conversion reaction is caused to be not thorough.5th, equipment seriously corroded, processing energy consumption are high.
Summary of the invention
In order to solve the above technical problem, the present invention provides turns in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical
Change method and system.The present invention has technical process convenient for control, is easy to industrialize that steady production, process costs are low, no three wastes
The features such as pollution and equipment are corroded.
The invention is realized by the following technical scheme:
Method for transformation containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including the use of transforming agent, by converting
Compounds containing sodium in aluminium electroloysis dangerous waste slag is transformed into not fluorine-containing soluble sodium chemical combination by the mechanochemistry conversion reaction in mill
Object, fluorochemical be transformed into insoluble and harmless minerals fluorine compounds, be oxidized containing cyanogen compound be transformed into it is harmless
N2Or NH3And CO2, to thoroughly release the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag;Conversion system includes successively connecting
The dangerous waste slag crushing plant that connects, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with
Concentration or crystallizer, drying or Equipment for Heating Processing are directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
Method for transformation containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including following some or all of step
(sequence of steps below is to express for convenience, does not indicate which part precedence relationship, contained step specifically include directly
It is subject to literal logical specification or logical relation):
(1) aluminium electroloysis dangerous waste slag is broken, milling, screening and homogenizing, obtain the dangerous waste ground-slag of particle≤200 μm;Point
Analyse the molal quantity or quality for determining sodium and fluorine in unit mass dangerous waste ground-slag;It analyzes and determines CN in unit mass dangerous waste ground-slag-
The molal quantity or quality of ion;
Abrasive body is added in conversion mill, then conversion is ground and carries out air emptying or N2Displacement, by the dangerous waste of metering
Ground-slag is added in conversion mill, and the mass ratio for controlling dangerous waste ground-slag and abrasive body is 1:(0.2~10), the water of metering is added to
In conversion mill, the solid-liquid mass ratio for controlling dangerous waste ground-slag and water is 1:(1~10);
By in dangerous waste ground-slag containing sodium, fluorochemical be converted to corresponding product chemistry stoichiometry 1~3 times of amount,
Or transforming agent is added in conversion mill by the amount of dangerous waste ground-slag quality 5~80%;
Grinding aid is added in conversion mill by the amount of dangerous waste ground-slag quality 0~1%;
(2) it completes to open conversion mill after step (1), the revolving speed of control conversion mill is 10~1000rpm, conversion temperature is
10~110 DEG C;In the conversion process, timing in batches is to slurry sampling analysis inspection, until Na in slurry solid formation+Ion contains
Amount meets company standard, solubility F-Ion concentration stops conversion mill when meeting national emission standard;
(3) slurry is transferred to stirred reactor (reaction kettle or reactive tank or reactor tank) after completion step (2) and carries out brokenly glue
With ripening, 60~150 DEG C of temperature is controlled, the processing time is 0.5~5h;
(4) by slurry that step (3) obtains using filtering or centrifuge separation mode is separated by solid-liquid separation and by aqueous solid phase
Object in conversion mill or stirred reactor (reaction kettle or reactive tank or reactor tank), using water be detergent by 1:(1~10) consolidate
Liquid quality than repeated several times dispensing laundry and be separated by solid-liquid separation, wash into solid formation soluble ion content meet enterprise mark
Until standard, merges separating liquid, respectively obtain the i.e. aqueous solid formation of mixture and solubility of wet fluorine-containing minerals and carbon
The weak solution of mixture;
(5) the aqueous solid formation that step (4) obtains is dried or is heat-treated 1 at a temperature of 80~300 DEG C~
10h, crushed to obtain the mixed powder material of fluorine-containing minerals and carbon again, the average particle size of mixed powder material≤
20 μm, which can be used as merchandise sales or further progress separating-purifying obtains high-quality carbon materials and fluorine
Compound mineral raw material;
The high temperature mixed powder material of fluorine-containing minerals and carbon being placed at a temperature of air atmosphere and 700~1200 DEG C
0.5~5h, the mixture that carbon component complete oxidation therein burns, its residue is fluorine-containing minerals are calcined in furnace;
(6) by the Dilute mixed solutions that step (4) obtains carry out concentration or crystallization treatment obtain mixture concentrated solution or
Person's solid-phase mixture, or Na, K, Li, Al, Mg, Ca compound separating-purifying in mixture are further obtained into more Gao Pin
The series compound raw material of matter and value;
(7) by CN in dangerous waste ground-slag-Ion conversion is at N2Or NH3And CO2Chemical reaction metering ratio 1~5 times of amount,
Perhaps by the amount of dangerous waste ground-slag quality 0.1~10% by cyanide transforming agent be added to or step (2) or step (3),
Or the oxidation containing cyanogen compound is converted to harmless N in step (6)2Or NH3And CO2.Timing carries out transformation system in batches
Analysis checks, until the CN in system-Ion concentration stops conversion reaction when meeting national emission standard;
(8) by generated NH in step (2) or step (3) or step (6)3、CO2、H2O gas carry out sorption enhanced and
Dry, generated reducibility gas is collected or direct oxidation burning.
Above-mentioned aluminium electroloysis dangerous waste slag contains F caused by referring in Aluminum Electrolysis Production-Ionic compound contains CN-Ion combination
Object is more than all solids waste of national emission standard.
There are Al, Al in above-mentioned aluminium electroloysis dangerous waste slag4C3, the substances such as AlN, Na, reaction institute is participated in conversion reaction
Imflammable gas (including the H of generation2、CH4、NH3Deng) it is reducibility gas described in step (8).
In above-mentioned conversion mill, the synchronous effect of high energy mechanical power is anti-in the mechanochemistry conversion containing sodium and fluorochemical
Answer so that solid particle is constantly ground, is levigate with conversion, make reactant and product constantly update from charcoal particle and
Removing, realizes the quick of conversion reaction and is properly completed.
Further, in all steps, pH control does not use protonic acid material for not less than 6, used to contain sodium
The transforming agent of compound and fluorochemical, cyanide transforming agent are free of chlorine element in grinding aid substance.
Further, the essential element that the dangerous waste cinder ladle includes is C (including graphitization C and non-graphitized C), Na, F,
It is two or more in Al, Ca, O, N, Li, Mg, Si, K, Fe;The compounds containing sodium includes NaF, Na3AlF6、NaCN、Na4
[Fe(CN)6] in it is two or more;The fluorochemical includes NaF, Na3AlF6、AlF3、LiF、CaF2、MgF2, in KF
It is two or more.
It further, include that Ca, Al, Mg, Sr, Ba, La, Ce each element are corresponding with the transforming agent of fluorochemical containing sodium
One or more of oxide, hydroxide, sulfate, nitrate, carbonate, acetate, citrate.
After being converted using transforming agent, the not fluorine-containing solubility of the correspondence that the compounds containing sodium in dangerous waste slag is transformed into contains sodium
Closing object includes NaOH, Na2SO4、NaNO3、NaOAc、Na2CO3、Na3C6H5O7、Na2AlO4、Na[Al(OH)6]2(OH)3、
NaAlSi2O6、Na2(H2SiO4)·7H2O、Na6Si8O19、Na2Al2SiO6、Na2Si2O5、Na2SiO3One or both of with
On.
After being converted using transforming agent, the insoluble and harmless minerals of the correspondence that the fluorochemical in dangerous waste slag is transformed into
Fluoride includes CaF2、MgF2、AlF3、SrF2、BaF2、CaF2、LaF3、CeF3、CeF4One or more of.
Further, the cyanide transforming agent includes Na2CO3·1.5H2O2、K2CO3·1.5H2O2、Na2O2、K2O2、
CaO2、SrO2、BaO2、H2O2、(NH4)2S2O8、Na2S2O8、K2S2O8、KMnO4、O2、O3One or more of.
Further, the grinding aid includes polymerized polyalcohol, polyalcohol amine, triisopropanolamine, ethylene glycol, the third two
One of alcohol, glycerine, diethylene glycol, triethanolamine, amide, stearic acid, oleic acid, calgon, odium stearate or two
Kind or more.
Further, the transforming agent, grinding aid be with the addition of solid, aqueous solution or gaseous state, using it is primary be added,
Or the mode for being added or being continuously added in batches.
Conversion system containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including sequentially connected dangerous waste slag are broken
Equipment, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with concentration or crystallizer,
Dry or Equipment for Heating Processing is directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
It further, further include condensing plant, condensing plant is connect with concentration or crystallizer.
It further, further include exhaust collection absorption equipment, exhaust collection absorption equipment grinds with milling equipment, conversion, stirs
Mix reactor, condensing plant is all connected with.
It further, further include storage facilities, storage facilities includes the dusty material storage arrangement connecting with disintegrating apparatus
And the storage arrangement of concentrate or crystalline product.
It further, further include analysis Instrument equipment, analysis Instrument equipment is anti-to milling equipment, conversion mill, stirring is derived from
The sample of the equipment such as device, concentration or crystallizer, drying or Equipment for Heating Processing, storage is answered to carry out analysis detection.
Further, the dangerous waste slag crushing plant include jaw crusher, cone crusher, pillar crusher,
Double-shaft crusher or impact disintegrating machine.
Further, the milling equipment include column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and with
The matched equipment for selecting dressing sieve point and homogenization, to obtain uniform, particle≤200 μm the dangerous waste ground-slag of composition.
Further, concentration or crystallizer are multiple-effect evaporation concentration or crystallization apparatus, for being concentrated or crystallizing solid-liquid point
Separating liquid from obtained soluble mixture is related to thermal energy and provides, evaporates the heat exchange and condensation, the recycling of condensed water of phase
Utilize, concentrate or transmission of crystal etc..
Above-mentioned exhaust collection absorption equipment is used for being crushed, being milled, sieving and being homogenized, and conversion reaction is broken glue and washed
Wash, be concentrated with crystallization etc. during generate tail gas be collected and absorption handle.Material composition in tail gas includes H2O、NH3、
CO2、H2、CH4、N2And micro dust;Gas phase H therein2O passes through condensation reuse, NH3、CO2, dust pass through absorbent absorb
It utilizes, fuel gas H2、CH4It is collected storage or enters combustion furnace as fuel utilization.
Material component detection, substance changing effect and content of the above-mentioned analysis Instrument equipment for each link of production process
Control detection, product quality detection, environmental emission standard monitoring.
Further, the described conversion mill is the air-tightness ball mill by transformation, body be equipped with abrasive body inlet and outlet,
Powder import, liquid material import, gas vent, slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body
For one or more of corundum ball, zirconia ball, porcelain ball, steel ball, stainless steel ball, alloying pellet.
The beneficial effects of the present invention are:
(1) present invention has technical process convenient for control, is easy to industrialize that steady production, production cost are low, not will cause
The features such as three-waste pollution and equipment are corroded.
(2) present invention solves the problems of existing wet-treating and pyrogenic attack production technology and deficiency.For
Aluminium electroloysis dangerous waste slag harmlessness and resource utilization, which utilize, provides a kind of advanced, system solution.
Detailed description of the invention
Fig. 1 is the process flow diagram of method for transformation of the present invention.
Fig. 2 is the structural schematic diagram of system of the present invention.
Fig. 3 is the x-ray diffraction pattern of aluminium electroloysis dangerous waste slag used by embodiment.
Fig. 4 is the x-ray diffraction pattern of the obtained fluorine minerals C of embodiment 1.
The SEM that Fig. 5 is the obtained mixed powder material B of embodiment 1 schemes.
Specific embodiment
Below with specific embodiment further illustrate technical solution of the present invention, but the invention is not limited to embodiment,
It is not intended to limit the scope of the invention.
As shown in Fig. 2, system of the invention includes sequentially connected dangerous waste slag crushing plant 1, milling equipment 2, conversion mill
3, stirred reactor 4 and solid-liquid separating equipment 5, solid-liquid separating equipment 5 are set with concentration or crystallizer 7, dry or heat treatment again
Standby 6 are directly connected to, and dry or Equipment for Heating Processing 6 connects disintegrating apparatus 8;It further include condensing plant 9, exhaust collection absorption equipment
10 and storage facilities, condensing plant 9 connect with concentration or crystallizer 7, exhaust collection absorption equipment 10 and milling equipment 2, turn
Change mill 3, stirred reactor 4, condensing plant 9 to be all connected with, storage facilities includes the dusty material storage dress connecting with disintegrating apparatus
Set the storage arrangement 12 of 11 and concentrate or crystalline product.
It further include analysis Instrument equipment, analysis Instrument equipment is to being derived from milling equipment, conversion mill, stirred reactor, concentration
Or the sample of the equipment such as crystallizer, drying or Equipment for Heating Processing, storage carries out analysis detection.
The dangerous waste slag crushing plant includes jaw crusher, cone crusher, pillar crusher, double-shaft crusher
Or impact disintegrating machine.
The milling equipment includes column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and matched choosing
Dressing sieve divides the homogenization equipment of powder, to obtain uniform, particle≤200 μm the waste cathode carbon powder of composition.
Concentration or crystallizer be multiple-effect evaporation be concentrated or crystallization apparatus, for be concentrated or crystallize be separated by solid-liquid separation obtain can
The separating liquid of soluble mixture is related to thermal energy and provides, evaporates the heat exchange and condensation, the recycling of condensed water, concentration of phase
Liquid or the transmission of crystal etc..
Above-mentioned exhaust collection absorption equipment, for broken, milling and homogenizing, glue and washing, concentration to be broken in conversion reaction
With crystallization etc. during generate tail gas be collected and absorption handle.Material composition in tail gas includes H2O、NH3、CO2、H2、
CH4、N2And micro dust;Gas phase H therein2O passes through condensation reuse, NH3、CO2, dust be absorbed and utilized by absorbent, can
Combustion gas body H2、CH4It is collected storage or enters combustion furnace as fuel utilization.
The described conversion mill is the air-tightness ball mill by transformation, body be equipped with abrasive body inlet and outlet, powder import,
Liquid material import, gas vent, slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body be corundum ball,
One or more of zirconia ball, porcelain ball, steel ball, stainless steel ball, alloying pellet.
Embodiment 1
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into
Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis
With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains
Amount.
(2) 200g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 45g CaSO4·2H2O、
2gCaO、1.5g Na2S2O8It is added in conversion mill and is uniformly mixed, use N2The air in conversion mill is replaced, then is added into conversion mill
Enter 300gH2O.Unlatching conversion mill, revolving speed 100rpm, temperature are 25 DEG C, and the conversion reaction time is 3h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 1000rpm, temperature are 95 DEG C, and constant temperature stirs
Reaction 90min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO
The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added
200gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2
Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it
Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon
Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 900 DEG C
Fluorine minerals C.
As seen from Figure 3, the main object of aluminium electroloysis dangerous waste slag used by embodiment 1 coordinate be divided into C, NaF,
Na3AlF6、AlF3、LiF、MgF2、SiC、Si3N4、Ca5MgSi3O12、Ca2SiO4、MgSiO3、CaSiO3。
As seen from Figure 4, it is by the main component that embodiment 1 handles the obtained Fluoride-bearing Ore substance C without charcoal
CaF2、MgF2、SiC、Si3N4、Al2O3、Al2SiO5、SiO2, illustrate NaF, Na in dangerous waste slag3AlF6、AlF3, the components such as LiF
It is totally converted metallogenic material CaF2And MgF2, carbon content is fully oxidized burning.
As seen from Figure 5, the mixed powder material B of obtained fluorine-containing minerals and carbon is handled by embodiment 1
Grain diameter be no more than 8 μm, particle be random pattern.
From these testing and analysis datas: embodiment 1 realize in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical it is complete
Full conversion, thoroughly relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.
Embodiment 2
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into
Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis
With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains
Amount.
(2) 300g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 30g MgSO4, 1g polyethylene
Alcohol, 4g K2S2O8It is added in conversion mill and is uniformly mixed, use N2Air in displacement conversion mill, then 400g is added into conversion mill
H2O.Unlatching conversion mill, revolving speed 500rpm, temperature are 40 DEG C, and the conversion reaction time is 2.5h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 700rpm, temperature are 105 DEG C, and constant temperature stirs
Reaction 100min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO
The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added
400gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2
Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it
Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon
Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 1000 DEG C
Fluorine minerals C.
The experimental results showed that embodiment 2 realizes the complete conversion in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, it is thorough
Bottom relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.
Embodiment 3
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into
Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis
With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains
Amount.
(2) 350g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 25g SrSO4、2g SrO2It is added
It is uniformly mixed into conversion mill, uses N2Air in displacement conversion mill, then 350g H is added into conversion mill2O.Unlatching conversion mill,
Revolving speed is 700rpm, temperature is 50 DEG C, and the conversion reaction time is 3.5h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 500rpm, temperature are 100 DEG C, and constant temperature stirs
Reaction 110min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO
The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added
350gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2
Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it
Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon
Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 950 DEG C
Fluorine minerals C.
The experimental results showed that embodiment 3 realizes the complete conversion in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, it is thorough
Bottom relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.
Claims (10)
1. the method for transformation in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, which is characterized in that including following part or
Overall Steps:
(1) aluminium electroloysis dangerous waste slag is broken, milling, screening and homogenizing, obtain the dangerous waste ground-slag of particle≤200 μm;Analysis is true
Determine the molal quantity or quality of sodium and fluorine in unit mass dangerous waste ground-slag;It analyzes and determines CN in unit mass dangerous waste ground-slag-Ion
Molal quantity or quality;
Abrasive body is added in conversion mill, then conversion is ground and carries out air emptying or N2Displacement, the dangerous waste ground-slag of metering is added
Enter into conversion mill, the mass ratio for controlling dangerous waste ground-slag and abrasive body is 1:(0.2~10), the water of metering is added to conversion mill
In, the solid-liquid mass ratio for controlling dangerous waste ground-slag and water is 1:(1~10);
By in dangerous waste ground-slag containing sodium, fluorochemical be converted to corresponding product chemistry stoichiometry 1~3 times of amount or
Transforming agent is added in conversion mill by the amount of dangerous waste ground-slag quality 5~80%;
Grinding aid is added in conversion mill by the amount of dangerous waste ground-slag quality 0~1%;
(2) complete to open conversion mill after step (1), the revolving speed of control conversion mill is 10~1000rpm, conversion temperature be 10~
110℃;In the conversion process, timing in batches is to slurry sampling analysis inspection, until Na in slurry solid formation+Ion concentration symbol
Close company standard, solubility F-Ion concentration stops conversion mill when meeting national emission standard;
(3) complete slurry is transferred to stirred reactor after step (2) and carry out broken glue and ripening, control 60~150 DEG C of temperature,
The processing time is 0.5~5h;
(4) slurry that step (3) obtains is separated by solid-liquid separation using filtering or centrifuge separation mode and aqueous solid formation is existed
Be detergent in conversion mill or stirred reactor, using water by 1:(1~10) solid-liquid mass ratio repeated several times dispensing laundry simultaneously
Be separated by solid-liquid separation, washing is until into solid formation, the content of soluble ion meets company standard, merge separating liquid, respectively obtain wet
Fluorine-containing minerals and carbon mixture, that is, aqueous solid formation and soluble mixture weak solution;
(5) the aqueous solid formation that step (4) obtains is dried or is heat-treated 1~10h, again at a temperature of 80~300 DEG C
It is crushed to obtain the mixed powder material of fluorine-containing minerals and carbon;
The mixed powder material of fluorine-containing minerals and carbon is placed in the high temperature furnace at a temperature of air atmosphere and 700~1200 DEG C
Calcine 0.5~5h, the mixture that carbon component complete oxidation therein burns, its residue is fluorine-containing minerals;
(6) Dilute mixed solutions that step (4) obtains are subjected to concentration or crystallization treatment obtains mixture concentrated solution or solid
Phase mixture;
(7) by CN in dangerous waste ground-slag-Ion conversion is at N2Or NH3And CO2Chemical reaction metering ratio 1~5 times of amount or press
Cyanide transforming agent is added to or step (2) or step (3) or step by the amount of dangerous waste ground-slag quality 0.1~10%
Suddenly the oxidation containing cyanogen compound is converted to harmless N in (6)2Or NH3And CO2.Timing carries out analysis inspection to transformation system in batches
It looks into, until the CN in system-Ion concentration stops conversion reaction when meeting national emission standard;
(8) by generated NH in step (2) or step (3) or step (6)3、CO2、H2O gas carries out sorption enhanced and drying,
Generated reducibility gas is collected or direct oxidation burning.
2. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
In all steps, pH control does not use protonic acid material, used compounds containing sodium and fluorine-containing chemical combination for not less than 6
The transforming agent of object, cyanide transforming agent are free of chlorine element in grinding aid substance.
3. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
The essential element that the dangerous waste cinder ladle includes is two or more in C, Na, F, Al, Ca, O, N, Li, Mg, Si, K, Fe;Described
Compounds containing sodium includes NaF, Na3AlF6、NaCN、Na4[Fe(CN)6] in it is two or more;The fluorochemical includes
NaF、Na3AlF6、AlF3、LiF、CaF2、MgF2, it is two or more in KF.
4. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
Compounds containing sodium and the transforming agent of fluorochemical include the corresponding oxide of Ca, Al, Mg, Sr, Ba, La, Ce each element, hydrogen-oxygen
One or more of compound, sulfate, nitrate, carbonate, acetate, citrate.
5. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
The cyanide transforming agent includes Na2CO3·1.5H2O2、K2CO3·1.5H2O2、Na2O2、K2O2、CaO2、SrO2、BaO2、
H2O2、(NH4)2S2O8、Na2S2O8、K2S2O8、KMnO4、O2、O3One or more of.
6. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
The grinding aid include polymerized polyalcohol, polyalcohol amine, triisopropanolamine, ethylene glycol, propylene glycol, glycerine, diethylene glycol,
One or more of triethanolamine, amide, stearic acid, oleic acid, calgon, odium stearate.
7. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that
The transforming agent, grinding aid with the addition of solid, aqueous solution or gaseous state, using it is primary be added or be added in batches or
The mode that person is continuously added to.
8. the conversion system in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, which is characterized in that including sequentially connected danger
Waste residue crushing plant, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with concentration or
Crystallizer, drying or Equipment for Heating Processing are directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
9. the conversion system in aluminium electroloysis dangerous waste slag according to claim 8 containing sodium, fluorochemical, which is characterized in that
It further include condensing plant, exhaust collection absorption equipment, storage facilities and analysis Instrument equipment, condensing plant is set with concentration or crystallization
Standby connection, exhaust collection absorption equipment are all connected with milling equipment, conversion mill, stirred reactor, condensing plant, storage facilities packet
Include the storage arrangement of the dusty material storage arrangement and concentrate or crystalline product that connect with disintegrating apparatus, analysis Instrument equipment pair
It is derived from the sample of milling equipment, conversion mill, stirred reactor, concentration or crystallizer, drying or Equipment for Heating Processing, storage facilities
Carry out analysis detection.
10. the conversion system in aluminium electroloysis dangerous waste slag according to claim 9 containing sodium, fluorochemical, which is characterized in that
The dangerous waste slag crushing plant is jaw crusher, cone crusher, pillar crusher, double-shaft crusher or impact type fining
Broken machine;The milling equipment is column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and matched selects dressing sieve
Divide the homogenization equipment of powder;The concentration or crystallizer is multiple-effect evaporation concentration or crystallization apparatus;The conversion mill
For by transformation air-tightness ball mill, body be equipped with abrasive body inlet and outlet, powder import, liquid material import, gas vent,
Slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body be corundum ball, zirconia ball, porcelain ball, steel ball,
One or more of stainless steel ball, alloying pellet.
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
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CN110470140A (en) * | 2019-08-30 | 2019-11-19 | 王一浩 | A kind of aluminium-scandium alloy smelting waste separation scandium oxide recovery furnace |
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Citations (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB208712A (en) * | 1922-12-21 | 1925-03-12 | Aluminum Co Of America | Improvements in or relating to methods of lining electrolytic cells for refining metals |
GB997370A (en) * | 1961-02-24 | 1965-07-07 | Electro Chimie Metal | Process for recovering fluorine values from the electrolytic production of aluminium |
JPH072517A (en) * | 1993-05-06 | 1995-01-06 | Onoda Kagaku Kogyo Kk | Production of anhydrous aluminum fluoride |
CN1583301A (en) * | 2004-05-24 | 2005-02-23 | 中国铝业股份有限公司 | Harmless treating method for waste tank lining of aluminium electrolytic bath |
CN101119943A (en) * | 2005-02-16 | 2008-02-06 | 诺沃福特国际有限公司 | Process and apparatus for converting spent potliners into a glass frit, and resulting products |
CN101444660A (en) * | 2008-12-30 | 2009-06-03 | 吴正建 | Innocent treatment of cyanide and fluoride in solid waste residues and recycling process thereof |
CN101804996A (en) * | 2010-04-02 | 2010-08-18 | 北京矿冶研究总院 | Method for recovering sodium fluoride from electrolytic aluminum waste cathode carbon block |
CN102992299A (en) * | 2012-12-04 | 2013-03-27 | 贵州铝城铝业原材料研究发展有限公司 | High temperature calcination method of electrolytic aluminum cathode scrap residue |
CN104768874A (en) * | 2012-04-12 | 2015-07-08 | 科瑞瑟斯有限公司 | Process and apparatus for obtaining material of value from a bauxite residue |
CN105821445A (en) * | 2016-05-27 | 2016-08-03 | 中南大学 | Method for recycling carbon and electrolytes from waste cathode carbon block of aluminum electrolytic cell |
CN205773365U (en) * | 2016-04-12 | 2016-12-07 | 郑州鸿跃环保科技有限公司 | A kind of aluminium electrolysis cell cathode carbon block reclaims the system of graphite |
CN107282598A (en) * | 2017-07-03 | 2017-10-24 | 李立安 | A kind of aluminium cell discards the recoverying and utilizing method of cathode carbon pieces |
-
2018
- 2018-08-01 CN CN201810867455.1A patent/CN109108049B/en active Active
Patent Citations (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
GB208712A (en) * | 1922-12-21 | 1925-03-12 | Aluminum Co Of America | Improvements in or relating to methods of lining electrolytic cells for refining metals |
GB997370A (en) * | 1961-02-24 | 1965-07-07 | Electro Chimie Metal | Process for recovering fluorine values from the electrolytic production of aluminium |
JPH072517A (en) * | 1993-05-06 | 1995-01-06 | Onoda Kagaku Kogyo Kk | Production of anhydrous aluminum fluoride |
CN1583301A (en) * | 2004-05-24 | 2005-02-23 | 中国铝业股份有限公司 | Harmless treating method for waste tank lining of aluminium electrolytic bath |
CN101119943A (en) * | 2005-02-16 | 2008-02-06 | 诺沃福特国际有限公司 | Process and apparatus for converting spent potliners into a glass frit, and resulting products |
CN101444660A (en) * | 2008-12-30 | 2009-06-03 | 吴正建 | Innocent treatment of cyanide and fluoride in solid waste residues and recycling process thereof |
CN101804996A (en) * | 2010-04-02 | 2010-08-18 | 北京矿冶研究总院 | Method for recovering sodium fluoride from electrolytic aluminum waste cathode carbon block |
CN104768874A (en) * | 2012-04-12 | 2015-07-08 | 科瑞瑟斯有限公司 | Process and apparatus for obtaining material of value from a bauxite residue |
CN102992299A (en) * | 2012-12-04 | 2013-03-27 | 贵州铝城铝业原材料研究发展有限公司 | High temperature calcination method of electrolytic aluminum cathode scrap residue |
CN205773365U (en) * | 2016-04-12 | 2016-12-07 | 郑州鸿跃环保科技有限公司 | A kind of aluminium electrolysis cell cathode carbon block reclaims the system of graphite |
CN105821445A (en) * | 2016-05-27 | 2016-08-03 | 中南大学 | Method for recycling carbon and electrolytes from waste cathode carbon block of aluminum electrolytic cell |
CN107282598A (en) * | 2017-07-03 | 2017-10-24 | 李立安 | A kind of aluminium cell discards the recoverying and utilizing method of cathode carbon pieces |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110358581A (en) * | 2019-08-16 | 2019-10-22 | 陕西延长石油(集团)有限责任公司 | A kind of aqueous dregs of fat are granulated again the device and method of pyrolytic gasification |
CN110470140A (en) * | 2019-08-30 | 2019-11-19 | 王一浩 | A kind of aluminium-scandium alloy smelting waste separation scandium oxide recovery furnace |
CN113429139A (en) * | 2021-06-27 | 2021-09-24 | 浙江红狮环保股份有限公司 | Method for cooperatively treating fluorine-containing inorganic compound by cement kiln |
CN113426807A (en) * | 2021-06-29 | 2021-09-24 | 云南云铝润鑫铝业有限公司 | Method for combined treatment and comprehensive utilization of resources of dangerous waste residues generated in aluminum electrolysis |
CN113426808A (en) * | 2021-06-29 | 2021-09-24 | 云南云铝润鑫铝业有限公司 | Method for recovering fluoride salt from aluminum electrolysis overhaul residues through pressurized alkaline leaching |
CN113426808B (en) * | 2021-06-29 | 2022-05-17 | 云南云铝润鑫铝业有限公司 | Method for recovering fluoride salt from aluminum electrolysis overhaul residues through pressurized alkaline leaching |
CN113426807B (en) * | 2021-06-29 | 2022-05-17 | 云南云铝润鑫铝业有限公司 | Method for combined treatment and comprehensive utilization of resources of dangerous waste residues generated in aluminum electrolysis |
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