AU2018216688A1 - Treatment of aqueous compositions including fines - Google Patents
Treatment of aqueous compositions including fines Download PDFInfo
- Publication number
- AU2018216688A1 AU2018216688A1 AU2018216688A AU2018216688A AU2018216688A1 AU 2018216688 A1 AU2018216688 A1 AU 2018216688A1 AU 2018216688 A AU2018216688 A AU 2018216688A AU 2018216688 A AU2018216688 A AU 2018216688A AU 2018216688 A1 AU2018216688 A1 AU 2018216688A1
- Authority
- AU
- Australia
- Prior art keywords
- composition
- consolidated material
- salt
- water
- water soluble
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000000203 mixture Substances 0.000 title claims abstract description 203
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 227
- 238000000034 method Methods 0.000 claims abstract description 218
- 230000008569 process Effects 0.000 claims abstract description 209
- 150000003839 salts Chemical class 0.000 claims abstract description 196
- 239000007787 solid Substances 0.000 claims abstract description 112
- 239000004576 sand Substances 0.000 claims abstract description 59
- 239000007864 aqueous solution Substances 0.000 claims abstract description 23
- 239000011362 coarse particle Substances 0.000 claims abstract description 20
- 239000000463 material Substances 0.000 claims description 146
- 229920000642 polymer Polymers 0.000 claims description 88
- 239000000243 solution Substances 0.000 claims description 56
- 229910052761 rare earth metal Inorganic materials 0.000 claims description 42
- 229920002401 polyacrylamide Polymers 0.000 claims description 38
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims description 19
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims description 19
- QGZKDVFQNNGYKY-UHFFFAOYSA-O ammonium group Chemical group [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 claims description 14
- 235000011130 ammonium sulphate Nutrition 0.000 claims description 13
- 230000003301 hydrolyzing effect Effects 0.000 claims description 13
- 238000001914 filtration Methods 0.000 claims description 12
- 230000005484 gravity Effects 0.000 claims description 12
- 150000001768 cations Chemical class 0.000 claims description 11
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical group [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims description 8
- 238000004064 recycling Methods 0.000 claims description 5
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 claims description 4
- 239000001099 ammonium carbonate Substances 0.000 claims description 4
- 235000019270 ammonium chloride Nutrition 0.000 claims description 4
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 claims description 3
- 235000012538 ammonium bicarbonate Nutrition 0.000 claims description 3
- MNNHAPBLZZVQHP-UHFFFAOYSA-N diammonium hydrogen phosphate Chemical compound [NH4+].[NH4+].OP([O-])([O-])=O MNNHAPBLZZVQHP-UHFFFAOYSA-N 0.000 claims description 3
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 claims description 2
- 239000004254 Ammonium phosphate Substances 0.000 claims description 2
- SWLVFNYSXGMGBS-UHFFFAOYSA-N ammonium bromide Chemical compound [NH4+].[Br-] SWLVFNYSXGMGBS-UHFFFAOYSA-N 0.000 claims description 2
- 235000012501 ammonium carbonate Nutrition 0.000 claims description 2
- 229910000148 ammonium phosphate Inorganic materials 0.000 claims description 2
- 235000019289 ammonium phosphates Nutrition 0.000 claims description 2
- -1 e.g. Substances 0.000 abstract description 26
- 238000002156 mixing Methods 0.000 abstract description 19
- 229920003169 water-soluble polymer Polymers 0.000 abstract description 4
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 58
- 239000002245 particle Substances 0.000 description 26
- 239000003245 coal Substances 0.000 description 18
- 229910052500 inorganic mineral Inorganic materials 0.000 description 14
- 235000010755 mineral Nutrition 0.000 description 14
- 239000011707 mineral Substances 0.000 description 14
- 239000002002 slurry Substances 0.000 description 14
- 238000012545 processing Methods 0.000 description 13
- 238000000605 extraction Methods 0.000 description 12
- 239000013535 sea water Substances 0.000 description 12
- 238000007596 consolidation process Methods 0.000 description 11
- 238000005065 mining Methods 0.000 description 11
- 239000012266 salt solution Substances 0.000 description 11
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 10
- 230000001965 increasing effect Effects 0.000 description 9
- 239000002253 acid Substances 0.000 description 8
- 238000004220 aggregation Methods 0.000 description 8
- 230000002776 aggregation Effects 0.000 description 8
- 239000003250 coal slurry Substances 0.000 description 8
- 239000007788 liquid Substances 0.000 description 8
- 239000002699 waste material Substances 0.000 description 8
- 239000010883 coal ash Substances 0.000 description 7
- 239000006228 supernatant Substances 0.000 description 7
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 6
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 6
- 229910019142 PO4 Inorganic materials 0.000 description 6
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 6
- 239000002956 ash Substances 0.000 description 6
- 238000005119 centrifugation Methods 0.000 description 6
- 230000007613 environmental effect Effects 0.000 description 6
- 230000003311 flocculating effect Effects 0.000 description 6
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 6
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 6
- 239000010452 phosphate Substances 0.000 description 6
- 235000021317 phosphate Nutrition 0.000 description 6
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 5
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 5
- 230000008901 benefit Effects 0.000 description 5
- 238000002474 experimental method Methods 0.000 description 5
- 239000010802 sludge Substances 0.000 description 5
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 4
- 239000001110 calcium chloride Substances 0.000 description 4
- 229910001628 calcium chloride Inorganic materials 0.000 description 4
- 239000004927 clay Substances 0.000 description 4
- 238000002485 combustion reaction Methods 0.000 description 4
- 229920001577 copolymer Polymers 0.000 description 4
- 238000002386 leaching Methods 0.000 description 4
- 239000001103 potassium chloride Substances 0.000 description 4
- 235000011164 potassium chloride Nutrition 0.000 description 4
- 238000003825 pressing Methods 0.000 description 4
- 230000002829 reductive effect Effects 0.000 description 4
- 238000012360 testing method Methods 0.000 description 4
- 229910052727 yttrium Inorganic materials 0.000 description 4
- VWQVUPCCIRVNHF-UHFFFAOYSA-N yttrium atom Chemical compound [Y] VWQVUPCCIRVNHF-UHFFFAOYSA-N 0.000 description 4
- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 229920002472 Starch Polymers 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 3
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 3
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 3
- 150000003863 ammonium salts Chemical class 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 239000011575 calcium Substances 0.000 description 3
- 239000003518 caustics Substances 0.000 description 3
- 239000003337 fertilizer Substances 0.000 description 3
- 239000008394 flocculating agent Substances 0.000 description 3
- 238000005189 flocculation Methods 0.000 description 3
- 230000016615 flocculation Effects 0.000 description 3
- 239000012530 fluid Substances 0.000 description 3
- 150000004676 glycans Chemical class 0.000 description 3
- 239000002608 ionic liquid Substances 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 3
- 239000003960 organic solvent Substances 0.000 description 3
- 229920001282 polysaccharide Polymers 0.000 description 3
- 239000005017 polysaccharide Substances 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 229910052706 scandium Inorganic materials 0.000 description 3
- SIXSYDAISGFNSX-UHFFFAOYSA-N scandium atom Chemical compound [Sc] SIXSYDAISGFNSX-UHFFFAOYSA-N 0.000 description 3
- 229910052708 sodium Inorganic materials 0.000 description 3
- 239000011780 sodium chloride Substances 0.000 description 3
- 239000002904 solvent Substances 0.000 description 3
- 235000019698 starch Nutrition 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-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
- IMNFDUFMRHMDMM-UHFFFAOYSA-N N-Heptane Chemical compound CCCCCCC IMNFDUFMRHMDMM-UHFFFAOYSA-N 0.000 description 2
- OFBQJSOFQDEBGM-UHFFFAOYSA-N Pentane Chemical compound CCCCC OFBQJSOFQDEBGM-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- QCWXUUIWCKQGHC-UHFFFAOYSA-N Zirconium Chemical compound [Zr] QCWXUUIWCKQGHC-UHFFFAOYSA-N 0.000 description 2
- MUBKMWFYVHYZAI-UHFFFAOYSA-N [Al].[Cu].[Zn] Chemical compound [Al].[Cu].[Zn] MUBKMWFYVHYZAI-UHFFFAOYSA-N 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 2
- LFVGISIMTYGQHF-UHFFFAOYSA-N ammonium dihydrogen phosphate Chemical compound [NH4+].OP(O)([O-])=O LFVGISIMTYGQHF-UHFFFAOYSA-N 0.000 description 2
- 239000010426 asphalt Substances 0.000 description 2
- 239000012267 brine Substances 0.000 description 2
- 229910052791 calcium Inorganic materials 0.000 description 2
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 description 2
- 125000002091 cationic group Chemical group 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000000701 coagulant Substances 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 239000000470 constituent Substances 0.000 description 2
- 238000010924 continuous production Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000000151 deposition Methods 0.000 description 2
- 238000004090 dissolution Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000005496 eutectics Effects 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 2
- 229910052737 gold Inorganic materials 0.000 description 2
- 239000010931 gold Substances 0.000 description 2
- 238000000227 grinding Methods 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 230000007062 hydrolysis Effects 0.000 description 2
- 238000006460 hydrolysis reaction Methods 0.000 description 2
- 238000011065 in-situ storage Methods 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(3+);trinitrate Chemical compound [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 description 2
- 229910052747 lanthanoid Inorganic materials 0.000 description 2
- 150000002602 lanthanoids Chemical class 0.000 description 2
- 239000011133 lead Substances 0.000 description 2
- 229910001629 magnesium chloride Inorganic materials 0.000 description 2
- YIXJRHPUWRPCBB-UHFFFAOYSA-N magnesium nitrate Chemical compound [Mg+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O YIXJRHPUWRPCBB-UHFFFAOYSA-N 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910000000 metal hydroxide Inorganic materials 0.000 description 2
- 150000004692 metal hydroxides Chemical class 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000011368 organic material Substances 0.000 description 2
- 235000006408 oxalic acid Nutrition 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 238000005191 phase separation Methods 0.000 description 2
- 238000005362 photophoresis Methods 0.000 description 2
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 description 2
- LWIHDJKSTIGBAC-UHFFFAOYSA-K potassium phosphate Substances [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- NIFIFKQPDTWWGU-UHFFFAOYSA-N pyrite Chemical compound [Fe+2].[S-][S-] NIFIFKQPDTWWGU-UHFFFAOYSA-N 0.000 description 2
- 229910052683 pyrite Inorganic materials 0.000 description 2
- 239000011028 pyrite Substances 0.000 description 2
- 238000005067 remediation Methods 0.000 description 2
- 238000005204 segregation Methods 0.000 description 2
- 229910052709 silver Inorganic materials 0.000 description 2
- 239000004332 silver Substances 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Chemical compound [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 2
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 2
- 239000002594 sorbent Substances 0.000 description 2
- 239000010414 supernatant solution Substances 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- 229910052726 zirconium Inorganic materials 0.000 description 2
- BNGXYYYYKUGPPF-UHFFFAOYSA-M (3-methylphenyl)methyl-triphenylphosphanium;chloride Chemical compound [Cl-].CC1=CC=CC(C[P+](C=2C=CC=CC=2)(C=2C=CC=CC=2)C=2C=CC=CC=2)=C1 BNGXYYYYKUGPPF-UHFFFAOYSA-M 0.000 description 1
- WWILHZQYNPQALT-UHFFFAOYSA-N 2-methyl-2-morpholin-4-ylpropanal Chemical compound O=CC(C)(C)N1CCOCC1 WWILHZQYNPQALT-UHFFFAOYSA-N 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 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
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 229910052692 Dysprosium Inorganic materials 0.000 description 1
- 229910052691 Erbium Inorganic materials 0.000 description 1
- 229910052693 Europium Inorganic materials 0.000 description 1
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical class [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 1
- 229910052688 Gadolinium Inorganic materials 0.000 description 1
- 229910052689 Holmium Inorganic materials 0.000 description 1
- 101000822443 Homo sapiens Selenocysteine lyase Proteins 0.000 description 1
- 238000004566 IR spectroscopy Methods 0.000 description 1
- 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 description 1
- 229910052765 Lutetium Inorganic materials 0.000 description 1
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical class [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 1
- 229910052779 Neodymium Inorganic materials 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 229920003171 Poly (ethylene oxide) Polymers 0.000 description 1
- 229920002873 Polyethylenimine Polymers 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 229910052777 Praseodymium Inorganic materials 0.000 description 1
- 229910052773 Promethium Inorganic materials 0.000 description 1
- 229910052772 Samarium Inorganic materials 0.000 description 1
- 102100022513 Selenocysteine lyase Human genes 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 229910052771 Terbium Inorganic materials 0.000 description 1
- 229910052775 Thulium Inorganic materials 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- 229910052769 Ytterbium Inorganic materials 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 235000019257 ammonium acetate Nutrition 0.000 description 1
- 229940043376 ammonium acetate Drugs 0.000 description 1
- BIGPRXCJEDHCLP-UHFFFAOYSA-N ammonium bisulfate Chemical compound [NH4+].OS([O-])(=O)=O BIGPRXCJEDHCLP-UHFFFAOYSA-N 0.000 description 1
- 229910000387 ammonium dihydrogen phosphate Inorganic materials 0.000 description 1
- 125000000129 anionic group Chemical group 0.000 description 1
- 229910001570 bauxite Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000010882 bottom ash Substances 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 229910001622 calcium bromide Inorganic materials 0.000 description 1
- WGEFECGEFUFIQW-UHFFFAOYSA-L calcium dibromide Chemical compound [Ca+2].[Br-].[Br-] WGEFECGEFUFIQW-UHFFFAOYSA-L 0.000 description 1
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 description 1
- 229910052729 chemical element Inorganic materials 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000002939 deleterious effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 230000001687 destabilization Effects 0.000 description 1
- 230000000368 destabilizing effect Effects 0.000 description 1
- QGBSISYHAICWAH-UHFFFAOYSA-N dicyandiamide Chemical compound NC(N)=NC#N QGBSISYHAICWAH-UHFFFAOYSA-N 0.000 description 1
- KBQHZAAAGSGFKK-UHFFFAOYSA-N dysprosium atom Chemical compound [Dy] KBQHZAAAGSGFKK-UHFFFAOYSA-N 0.000 description 1
- 238000000909 electrodialysis Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- UYAHIZSMUZPPFV-UHFFFAOYSA-N erbium Chemical compound [Er] UYAHIZSMUZPPFV-UHFFFAOYSA-N 0.000 description 1
- OGPBJKLSAFTDLK-UHFFFAOYSA-N europium atom Chemical compound [Eu] OGPBJKLSAFTDLK-UHFFFAOYSA-N 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 238000000915 furnace ionisation nonthermal excitation spectrometry Methods 0.000 description 1
- UIWYJDYFSGRHKR-UHFFFAOYSA-N gadolinium atom Chemical compound [Gd] UIWYJDYFSGRHKR-UHFFFAOYSA-N 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- KJZYNXUDTRRSPN-UHFFFAOYSA-N holmium atom Chemical compound [Ho] KJZYNXUDTRRSPN-UHFFFAOYSA-N 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 239000003456 ion exchange resin Substances 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 description 1
- 229910000360 iron(III) sulfate Inorganic materials 0.000 description 1
- YDZQQRWRVYGNER-UHFFFAOYSA-N iron;titanium;trihydrate Chemical compound O.O.O.[Ti].[Fe] YDZQQRWRVYGNER-UHFFFAOYSA-N 0.000 description 1
- 239000010977 jade Substances 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 230000002147 killing effect Effects 0.000 description 1
- 229910052746 lanthanum Inorganic materials 0.000 description 1
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 230000000670 limiting effect Effects 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- OHSVLFRHMCKCQY-UHFFFAOYSA-N lutetium atom Chemical compound [Lu] OHSVLFRHMCKCQY-UHFFFAOYSA-N 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- OTCKOJUMXQWKQG-UHFFFAOYSA-L magnesium bromide Chemical compound [Mg+2].[Br-].[Br-] OTCKOJUMXQWKQG-UHFFFAOYSA-L 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 235000019837 monoammonium phosphate Nutrition 0.000 description 1
- 239000000178 monomer Substances 0.000 description 1
- QEFYFXOXNSNQGX-UHFFFAOYSA-N neodymium atom Chemical compound [Nd] QEFYFXOXNSNQGX-UHFFFAOYSA-N 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 1
- 229920000371 poly(diallyldimethylammonium chloride) polymer Polymers 0.000 description 1
- 229920001467 poly(styrenesulfonates) Polymers 0.000 description 1
- 229920000768 polyamine Polymers 0.000 description 1
- 229920000867 polyelectrolyte Polymers 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 235000010333 potassium nitrate Nutrition 0.000 description 1
- 239000004323 potassium nitrate Substances 0.000 description 1
- 235000011009 potassium phosphates Nutrition 0.000 description 1
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical class [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 description 1
- 235000011151 potassium sulphates Nutrition 0.000 description 1
- PUDIUYLPXJFUGB-UHFFFAOYSA-N praseodymium atom Chemical compound [Pr] PUDIUYLPXJFUGB-UHFFFAOYSA-N 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- VQMWBBYLQSCNPO-UHFFFAOYSA-N promethium atom Chemical compound [Pm] VQMWBBYLQSCNPO-UHFFFAOYSA-N 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- KZUNJOHGWZRPMI-UHFFFAOYSA-N samarium atom Chemical compound [Sm] KZUNJOHGWZRPMI-UHFFFAOYSA-N 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 235000010344 sodium nitrate Nutrition 0.000 description 1
- 239000004317 sodium nitrate Substances 0.000 description 1
- 239000001488 sodium phosphate Substances 0.000 description 1
- 235000011008 sodium phosphates Nutrition 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000010561 standard procedure Methods 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- GZCRRIHWUXGPOV-UHFFFAOYSA-N terbium atom Chemical compound [Tb] GZCRRIHWUXGPOV-UHFFFAOYSA-N 0.000 description 1
- FRNOGLGSGLTDKL-UHFFFAOYSA-N thulium atom Chemical compound [Tm] FRNOGLGSGLTDKL-UHFFFAOYSA-N 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N titanium dioxide Inorganic materials O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- FZGFBJMPSHGTRQ-UHFFFAOYSA-M trimethyl(2-prop-2-enoyloxyethyl)azanium;chloride Chemical compound [Cl-].C[N+](C)(C)CCOC(=O)C=C FZGFBJMPSHGTRQ-UHFFFAOYSA-M 0.000 description 1
- RRHXZLALVWBDKH-UHFFFAOYSA-M trimethyl-[2-(2-methylprop-2-enoyloxy)ethyl]azanium;chloride Chemical compound [Cl-].CC(=C)C(=O)OCC[N+](C)(C)C RRHXZLALVWBDKH-UHFFFAOYSA-M 0.000 description 1
- 238000005292 vacuum distillation Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- NAWDYIZEMPQZHO-UHFFFAOYSA-N ytterbium Chemical compound [Yb] NAWDYIZEMPQZHO-UHFFFAOYSA-N 0.000 description 1
- 229910052845 zircon Inorganic materials 0.000 description 1
- GFQYVLUOOAAOGM-UHFFFAOYSA-N zirconium(iv) silicate Chemical compound [Zr+4].[O-][Si]([O-])([O-])[O-] GFQYVLUOOAAOGM-UHFFFAOYSA-N 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
- B09B1/00—Dumping solid waste
-
- 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
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/38—Stirring or kneading
-
- 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
- B09B3/80—Destroying solid waste or transforming solid waste into something useful or harmless involving an extraction step
-
- 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
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
- C02F11/148—Combined use of inorganic and organic substances, being added in the same treatment step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/10—Nature of the water, waste water, sewage or sludge to be treated from quarries or from mining activities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
- C02F2103/365—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Treatment Of Sludge (AREA)
- Processes Of Treating Macromolecular Substances (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
Processes of consolidating aqueous compositions including fines and process water are disclosed. The processes include mixing the composition with a highly water soluble salt or an aqueous solution thereof to destabilize and consolidate solids in the compositions, e.g., to destabilize and consolidate fines, and separating the consolidated solids from the process water. A water soluble polymer and coarse particles, e.g., sand, can also be used in the treatment of the compositions.
Description
TREATMENT OF AQUEOUS COMPOSITIONS
INCLUDING FINES
CROSS-REFERENCE TO RELATED APPLICATIONS [0001] This application claims the benefit of U.S. Provisional Application No.
62/452784, filed 31 January 2017; U.S. Provisional Application No. 62/535398, filed 21 July 2017; U.S. Provisional Application No. 62/554220, filed 5 September 2017; and U.S. Provisional Application No. 62/583360, filed 8 November 2017; the entire disclosures of each of which are hereby incorporated by reference herein.
TECHNICAL FIELD [0002] The present disclosure relates to dewatering and consolidation of aqueous compositions including fines such as tailings from processing ore.
BACKGROUND [0003] Various mining and extraction processes produce a tailings stream characterized as a slurry of particulate matter in water. These tailings often contain components that are hazardous and cannot be discharged directly into rivers and streams. A common practice is to store tailings in ponds, which can be very large or encompass numerous sites. For example, it has recently been estimated that Canadian oil-sands tailings ponds cover an area of about 200 square kilometers. In the U.S., the Environmental Protection Agency has identified more than 500 ash and coal slurry ponds, mostly in the Appalachian coal mining region. In Florida, phosphate mining results in the production of approximately 100,000 tons a day of phosphatic clays in the form of a slurry that is also stored in ponds. It is very difficult to dewater and the phosphate industry leaves about 40% of mined land in unstable clay settling areas. The processes for mining and extracting of ores of aluminum, copper, zinc, lead, gold, silver, etc., also create tailing streams.
[0004] The management and sustainability of tailings ponds pose significant and growing problems. The dams or impoundments used to form the ponds are often constructed from local material and are a significant potential danger. The failure of a coal slurry dam in West Virginia resulted in the Buffalo Creek flood, which killed more than 125 people. Various other, more
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PCT/US2018/015423 recent, dam failures in tailings containment ponds have resulted in significant if not catastrophic environmental damage. For example, in 2016 the failure of a tailings dam in Henan province, China, released about 2 million cubic meters of red mud, totally immersing a nearby village. In 2015, a waste heap from Jade mining failed in Myanmar, killing at least 113 people.
[0005] In the oil sands industry, fines are defined as particles having a diameter equal to or less than 44 pm. They are part of a waste stream that settles much more slowly than coarse sand, leaving a layer of water with some entrained fines near the surface of the ponds. This water is reused in the bitumen extraction process. Initially, most of the fines (mainly silica and clay particles) form an intermediate layer of so-called fluid fine tailings (FFT). This fluid has a low solids content, between 15% and 30% and is also referred to as thin fine tailings (TFT). Over time, additional settling occurs, but the negative surface charge of the mineral particles limits aggregation and a distinct layer of so-called mature fine tailings (MFT) is formed. The solids content of the MFT is on average about 30%, but varies with depth. It has gel-like properties that make it difficult to handle and dewater. It has been estimated that under the action of gravityalone, this tailings component could take decades to centuries to consolidate and settle and thus allow for land reclamation. The tailings from phosphate mining in Florida form a similar gel-like structure. Beneath a surface crust, these tailings have about a 25% solids content with a fluidlike consistency.
[0006] So-called impoundment ponds are used to store two types of waste from coal handling and combustion. Coal ash that is a residue of combustion is one such material and include several components (fly ash, bottom ash, etc.). The EPA estimated that 100 million tons of coal ash was generated in the U.S. in 2012. There are dry methods of disposal and coal ash can also be recycled into building material, but for economic reasons the wet disposal of ash into ash ponds has been common practice. The EPA estimated that there are more than 500 units, presumably ash ponds, at more than 200 power plants. There are increasing environmental concerns regarding leachate from these ponds.
[0007] The second type of impoundment pond for coal processing wastes stores material that is a product of coal preparation plants, where soil and rock are removed from run-of-mine coal to lower its ash content and increase its value. This is accomplished by washing. However, this coal cleaning process produces a reject stream in the form of a sludge or slurry. This slurry
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PCT/US2018/015423 contains very fine coal particles together with other material (such as clays) and, as with the tailings streams mentioned above, is very difficult to dewater economically using standard methods. There are now about 600 so-called slurry impoundments in the U.S. where this waste material is stored, mostly in the Appalachian coal mining region. The impoundments can be as large as 50 acres in size and contain billions of gallons of toxic sludge. This material represents both an economic cost in terms of the loss of a valuable resource (in the form of coal fines) and a major environmental hazard. The Washington Post (April 24, 2013) reported that a study by the Office of Surface Mining Reclamation and Enforcement found that many sludge impoundment walls are weak and are known to leak. Historically, a number of catastrophic failures of ash and sludge ponds have occurred, resulting in significant loss of life and environmental devastation. With the coal industry in decline and mining companies filing for bankruptcy, the impoundment ponds, both those that remain in use and those that have been abandoned, are a significant and growing problem.
[0008] The production of alumina from bauxite also results in the generation of a large tailings stream. Approximately 77 million tons of a highly alkaline waste product composed mainly of iron oxide and known as red sludge or red mud is generated every year. This poses a significant disposal problem and a tailings dam failure led to catastrophic consequences, as described above.
[0009] There is a continuing need to manage and treat aqueous fines, e.g., tailings, to reduce the volume of such tailings and/or to dewater and consolidate solids in such tailings and in a manner preferable for land reclamation and remediation.
SUMMARY OF THE DISCLOSURE [0010] Advantages of the present disclosure include processes to dewater aqueous compositions including fines, e.g., tailings, to produce high solids content materials.
[0011] These and other advantages are satisfied, at least in part, by a process of consolidating solids in the aqueous composition. The process comprises treating the composition, which includes fines and process water, with a highly water soluble salt. Advantageously, the process can include treating the composition with at least one highly water soluble salt or solution thereof and can optionally include either or both of (i) at least one
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PCT/US2018/015423 polymer flocculant or solution thereof and/or (ii) optionally coarse particles, e.g., sand, to form a treated composition. The treated composition can include a consolidated material in the process water, which can then advantageously be separated from the consolidated material.
[0012] Implementations of the process of the present disclosure include, for example, (i) treating the composition with at least one highly water soluble salt to form a treated composition including a consolidated material m the process water, (ii) treating the composition with at least one highly water soluble salt and at least one polymer flocculant to form a treated composition including a consolidated material in the process water, (iii) treating the composition with at least one highly water soluble salt and coarse particles to form a treated composition including a consolidated material in the process water, and (iv) treating the composition with at least one highly water soluble salt, at least one polymer flocculant and coarse particles to form a treated composition including a consolidated material in the process water. Each of these implementations can include aqueous solutions of the salt and/or polymer flocculant to treat the composition. Each of these implementations can include separating the process water from the consolidated material. Advantageously, the consolidated material has a density greater than the process water.
[0013] Embodiments of the processes include one or more of the following features individually or combined. For example, the aqueous composition including fines can be tailings. In some embodiments, the at least one highly water soluble salt can have a solubility in water (a salt/water solubility) of at least about 5 g/100 g at 20 °C, e.g., at least about 10 g/'100 g at 20 °C. In other embodiments, the at least one highly water soluble salt is a non-hydrolyzing salt. In still further embodiments, the at least one highly water soluble salt can have a monovalent cation and can include an ammonium based salt, a phosphate based salt, or a sulfate based salt or combinations thereof.
[0014] In certain embodiments, the treated composition can have a salt-composition concentration of at least 0.5 wt% of the at least one highly water soluble salt and preferably no less than about 1 wt%, such as at least about 2 wt% and even greater than about 3 wt%, 4 wt%, 5 wt%, etc. of the at least one highly water soluble salt. In some embodiments, the at least one polymer flocculant is a polyacrylamide or co-polymer thereof. The treated composition can have a polymer-composition concentration of the at least one polymer flocculant of no less than about
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PCT/US2018/015423
0.001 wt%, e.g., no less than about 0.003 wt%, 0.005 wt%, 0.01 wt% or 0.04 wt%. In other embodiments, the composition is treated with coarse particles, e.g., sand, at a sand to fines ratio of less than 4:1, e.g., between about 2.5:1.0 to about 0.5:1 or between about 2.25:1 to about 0.75:1. Advantageously, the polymer flocculant forms high density flocs, e.g., having a density greater than the process water, which facilitates separation and dewatering of the consolidated solids.
[0015] In various embodiments, treating the composition can include combining the composition with a solution including the at least one highly water soluble salt and the at least one polymer flocculant. In some embodiments, treating the composition can include combining a stream of the composition, e.g,, tailings, with a stream of a solution including the at least one highly water soluble salt and a separate stream of a solution including the at least one polymer flocculant. Alternatively, or in combination, treating the composition can include combining a stream of the composition, e.g., tailings, with a stream of a solution including both the at least one highly water soluble salt and the at least one polymer flocculant. Coarse particles (e.g., sand) can also be added to the composition or stream thereof and/or to any or all of the solution streams. Advantageously, the streams can be mixed inline and/or with the aid of an inline mixer. In certain embodiments, treating the composition can be carried out at a temperature of no more than 50 °C, e.g., no more than about 40 °C or about 30 °C. In other embodiments, treating the composition includes using a solution of one or more highly soluble salts sourced from a natural or existing source such as seawater or a body of hypersaline water.
[0016] In still further embodiments, the process water can be separated from the consolidated material by any one or more of decanting, filtering, vacuuming, gravity draining, electrofiltering, etc. or combinations thereof. In various embodiments, separating the process water from the consolidated material can include mechanically dewatering the consolidated material, e.g., mechanically dewatering the consolidated material by a dewatering screw. Once separated, the consolidated material can be transferred for further dewatering or disposal.
[0017] In practicing aspects of the processes of the present disclosure and the various embodiments thereof, the separated process water can include the at least one highly water soluble salt and the process can further comprise recovering at least a portion of the separated process water. In some embodiments, the process can further comprise recycling at least a
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PCT/US2018/015423 portion of the recovered separated process water to treat additional tailings. In other embodiments, the process can further include purifying at least a portion of the recovered process water.
[0018] Yet another aspect of the present disclosure includes recovering valuable materials from the aqueous composition of fines, e.g., tailings. The valuable materials can include rare earth elements (REE) associated with solids such as clays m tailings from various types of aqueous fines such as tailings stream. Therefore, m practicing certain aspects of the processes of the present disclosure and the various embodiments thereof the aqueous compositions can further include rare earth element materials which can be recovered by treating the composition with at least one highly water soluble salt, e.g., an ammonium based salt such as ammonium sulfate, to form a treated composition including REE in the process water and/or in the consolidated materials. In some embodiments, the process further includes separating the process water from the consolidated material and recovering the REE from the separated process water and/or the consolidated materials.
[0019] Advantageously, the processes of the present disclosure can consolidate the solids of the composition to produce a consolidated material having a solids content in excess of about 45% by weight, e.g., a solids content of greater than about 50% and higher than about 60%, 65%, 70% and 75% by weight.
[0020] In practicing certain aspects of the processes of the present disclosure and the various embodiments thereof, the consolidated material formed in the treated composition according to certain embodiments can result in a high solids content after mixing and/or dewatering the treated composition in a short period of time. In some embodiments, the consolidated material can have a solids content of greater than about 50% and at least about 60%, 65%, 70%, 75% and 80% by weight after mixing and/or dewatering.
[0021] Another aspect of the present disclosure includes an aqueous solution for treating aqueous fines. The aqueous solution includes a highly water soluble ammonium based salt and a polymer flocculant, e.g., a water soluble polymer. Embodiments include, together or individually, an aqueous solution of one or more of the highly water soluble salt(s) and having a concentration of no less than about 1 wt%, e.g., at least about 2 wt%, 5 wt%, 10 wt%, 20 wt%, 30 wt% and even as great as a 40 wt% or as an aqueous salt slurry. The aqueous solution can
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PCT/US2018/015423 also include one or more of the polymer flocculant(s) and having a concentration of no less than about 0.005 wt%, e.g. no less than about 0.01 wt%, 0.04 wt%, 0.05 wt %, 0.1 wt%, 0.2 wt%, 0.4 wt%, for example [0022] Additional advantages of the present invention will become readily apparent to those skilled in this art from the following detailed description, wherein only the preferred embodiment of the invention is shown and described, simply by way of illustration of the best mode contemplated of carrying out the invention. As will be realized, the invention is capable of other and different embodiments, and its several details are capable of modifications m various obvious respects, all without departing from the invention. Accordingly, the drawings and description are to be regarded as illustrative in nature, and not as restrictive.
BRIEF DESCRIPTION OF THE DRAWINGS [0023] Reference is made to the attached drawings, wherein elements having the same reference numeral designations represent similar elements throughout and wherein:
[0024] Figure 1 schematically illustrates an exemplar}/ embodiment of a process of consolidating an aqueous composition including fines and process water.
[0025] Figure 2 shows pictures of vials containing waste coal slurry treated according to an embodiment of the present disclosure. The pictures show coal slurry after adding an ionic solution (left), then centrifuging (middle) and after removal of supernatant solution (right).
[0026] Figure 3 shows pictures of the dewatered coal slurry from Figure 2 after removal from the vial (left) and subsequent hand-pressing between paper towels.
[0027] Figure 4 shows pictures of vials containing mature fine tailings from oil sands processing treated with an ammonium salt solution including a polyacrylamide flocculant at the concentrations indicated in the figure.
[0028] Figure 5 shows pictures of vials containing mature fine tailings treated with an ammonium salt and a polyacrylamide flocculant and illustrate effects of increasing salt concentration and reducing polymer concentration under the conditions tested.
[0029] Figure 6 shows a picture of vials containing mature fine tailings from oil sands processing treated with seawater which included varying amounts of a polyacrylamide flocculant.
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PCT/US2018/015423
DETAILED DESCRIPTION OF THE DISCLOSURE [0030] The present disclosure relates to treating aqueous composition including fines to consolidate and dewater the composition. Aqueous compositions of fines can be in the form of tailings, which are typically produced when mining and processing ores such as metal ores, e.g., aluminum, copper, zinc, lead, gold, silver, etc., phosphate ore, oil sands, etc. Aqueous compositions of fines can also be produced when processing coal. For example, certain processes finely grind coal prior to combustion to more readily liberate pyrite (a sulfur based compound) and hence reduce sulfur emissions upon combustion of the ground coal. Such processes can produce fine coal particles as well as other fine mineral or mineral matter in an aqueous composition that are difficult to recapture and reuse.
[0031] The particulate solids in the aqueous compositions of the present disclosure can be minerals and mineral like materials, i.e., mineral matter, clays, slit, and in sizes ranging from fines to coarse solids. The term fines as used herein is consistent with the Canadian oil sands classification system and means solid particles with sizes equal to or less than 44 microns (pm). Sand is considered solid particles with sizes greater than 44 pm. The composition of the fines depends on the source of the materials, but generally fines are comprised mostly of silt and clay material and sometimes minerals or mineral matter, depending on the ore. Tailings can have various solids contents and various amounts of fines as its solids content. The tailings treated according to embodiments of the present disclosure can include a significant amount of fines by weight (>5 wt%) as their solids content. Such tailings can include at least about 10 wt%, 20 wt%, 30 wt%, 40 wt%, 50 wt%, 60 wt%, 70 wt% or higher fines as their solids content.
[0032] Advantageously, the process of the present disclosure can consolidate the solids of aqueous compositions including fines, e.g., tailings, to produce consolidated material having a solids content in excess of about 45% by weight, e.g., a solids content of greater than about 70% by weight.
[0033] The terms coagulation and flocculation are often used interchangeably in the literature. As used herein, however, coagulation means particle aggregation brought about by the addition of hydrolyzing salts, whereas flocculation means particle aggregation induced by flocculating polymers. Hydrolyzing salts undergo hydrolysis when added to water to form metal hydroxides, which precipitate from the solution, trapping fines and other minerals in the
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PCT/US2018/015423 coagulating mass. Hydrolyzing salts typically have low solubility in water and are used as coagulants. Aggregation induced by flocculation, in contrast, is believed to be the result of the polymer binding to the particles thereby tying the particles together into a so called floc causing aggregation of the particles.
[0034] In practicing aspects of the present disclosure, an aqueous composition of fines and process water can be consolidated by treating the composition with one or more highly water soluble salt(s) or an aqueous solution thereof to destabilize and consolidate solids in the composition, e.g., to destabilize and consolidate fines in the composition. Aggregation induced by the addition of salts is believed to be the result of destabilizing the particles suspended in the fluid by an alteration or a shielding of the surface electrical charge of the particles to reduce the inter-particle repulsive forces that prevent aggregation. In certain embodiments, the composition is tailings, e.g., a suspension of particulate solids in an aqueous liquid which include fines and process water such as tailings streams from metal extraction or a coal slurry which includes fines of coal and other matter. The process includes treating the composition with the highly water soluble salt(s) or an aqueous solution thereof to form a treated composition including a consolidated material, e.g. consolidated fines, in process water. The process water can then be separated from the consolidated material. Advantageously, the consolidated material has a solids content of at least 45% bv weight, e.g., a solids content of greater than about 50% and higher than about 60%, 65%, 70% and 75% by weight.
[0035] Salts that are useful in practicing the present disclosure include salts that are highly soluble in water. A highly water soluble salt as used herein is one that has a solubility' in water of greater than 2 g of salt per 100 g of water (i.e., a salt/water solubility of 2g/100g) at 20 °C. Preferably the highly water soluble salt has a water solubility of at least about 5 g/100 g at 20 °C, e.g., at least about 10 g/100 g of salt/water at 20 °C.
[0036] In addition, the highly water soluble salts used in the processes of the present disclosure are preferably non-hydrolyzing. Hydrolyzing salts undergo hydrolysis when added to water to form metal hydroxides, which precipitate from the solution. Such hydrolyzing salts are believed to form open flocs with inferior solids content and cannot be readily recycled for use with additional tailings in continuous or semi-continuous processes. In addition, hydrolyzing salts typically have low solubility in water and are used at elevated temperatures to ensure
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PCT/US2018/015423 sufficient solubility for aggregation, which is an energy intensive process. See US 4,225,433 which discloses the use of lime as a coagulating agent at a temperature of 75 °C.
[0037] Further, the highly water soluble salts are preferably not carboxylate salts since such organic acid salts tend to be more expensive than inorganic salts and can be deleterious to plant and/or animal life.
[0038] Highly water soluble salts that are not hydrolyzing and useful in practicing processes of the present disclosure include salts having a monovalent cation, e.g., alkali halide salts such as sodium chloride, potassium chloride; also salts with monovalent cations such as sodium nitrate, potassium nitrate, sodium and potassium phosphates, sodium and potassium sulfates, etc, are useful in practicing processes of the present disclosure. Other monovalent cationic salts useful in practicing processes of the present disclosure include ammonium based salts such as ammonium acetate (NH4C2H3O2), ammonium chloride (NH4CI), ammonium bromide (NH4.Br), ammonium carbonate ((NH/COs), ammonium bicarbonate (NH4HCO3), ammonium nitrate (NH4NO3), ammonium sulfate ((^-14)28()4), ammonium hydrogen sulfate (NH4HSO4), ammonium dihydrogen phosphate (NH4H2PO4), ammonium hydrogen phosphate ((NF/h-HPCL), ammonium phosphate ((NIL/PCh), etc. Mixtures of such salts can also be used.
[0039] Ammonium based salts are useful for practicing the present disclosure since residual ammonium based salts on the consolidated material after combining the salt with the aqueous fines, e.g., tailings, can be beneficial to plant life. In fact, many of the ammonium based salts are useful as fertilizers, e.g., ammonium chloride, ammonium nitrate, ammonium sulfate, etc. Many of the monovalent sulfate and phosphate salts are also useful as fertilizers. In certain embodiments of the present disclosure, the highly water soluble salt or salts used in the processes of the present disclosure can preferably be non-toxic and beneficial to plant life to aid in environmental remediation and the restoration of mine sites.
[0040] In one aspect of the present disclosure, treating the compositions of the present disclosure with a highly water soluble salt destabilizes and consolidates solids in the composition. Such a process can include mixing the composition, which includes fines and process water, with a highly water soluble salt to consolidate the fines, and separating the process water from the consolidated fines to produce a high solids content, e.g., at least 45% by weight. In certain embodiments, the highly water soluble salt is an ammonium based salt.
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PCT/US2018/015423 [0041] Highly water soluble salts that can be used in practicing the present process can also include salts having multivalent cations. Such salts include, for example, divalent cation salts such as calcium and magnesium cation salts, such as calcium chloride (CaCb), calcium bromide (CaBr/), calcium nitrate (Ca(NOs)2), magnesium chloride (MgCh), magnesium bromide (MgBr2), magnesium nitrate (MgtNChb), magnesium sulfate (MgSCU); and trivalent cation salts such as aluminum and iron (III) cation salts, e.g., aluminum chloride (AICI3), aluminum nitrate (Ai(N()-<)-<).. aluminum sulfate (Ah/SCLY), iron (III) chloride (FeCh), iron (III) nitrate (FefNOsY), iron (III) sulfate ^62(8()4)3, etc. As explained above, the highly water soluble salts used in the processes of the present disclosure are preferably non-hydrolyzing. Many of the multivalent cation salts are hydrolyzing and thus less preferred for the reasons stated above. Moreover, experimentation with multivalent salts showed increased fouling of containers and formation of less cohesive consolidated materials as compared to highly water soluble salts having monovalent cations. In addition, some multivalent salts, such as FeCh and Fe2(SO/;)3, are particularly corrosive and Fe2(SC>4)3 is formed from oxidizing pyrite and results in acid mine runoff, which make such salts less preferable for use in processes of the present disclosure.
[0042] When a sufficiently high concentration of the highly water soluble salt is included in the treated composition, the salt can destabilize and consolidate solids in the composition. For a relatively short process times with a relatively low energy input, the salt-composition concentration of the at least one highly water soluble salt should preferably be at least 0.5 wt% and preferably no less than about 1 such as at least about 2 wt% and even at least about 3 wt%, 4 wt%, 5 wt%, etc. The term “salt-composition concentration” as used herein refers to the concentration of the highly water soluble salt(s) in the treated aqueous fines, e.g., tailings, and is determined by taking the percentage of the mass of highly water soluble salt(s) divided by the combined mass of the salt(s) plus the aqueous fines and any water used to dilute the salt(s). For example, combining 1 part undiluted (i.e., neat) salt to 99 parts tailings by weight results in a salt-composition concentration of 1 wt%. Alternatively, treating tailings with an equal weight of a 2 wt% solution of the salt also results in a salt-composition concentration of 1 wt% in the treated tailings.
[0043] The highly water soluble salt(s) can be used to treat compositions of the present disclosure as a solid, e.g., combining the salt as a powder with the composition. Alternatively,
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PCT/US2018/015423 the salt can be used to treat as a solution, e.g., combining an aqueous salt solution with the compositions. In some aspects of the present disclosure, an aqueous solution of the highly water soluble salt can be prepared having a concentration of no less than about 1 wt%, e.g., greater than about 2 wt%, 5 wt%, 10 wt%, 20 wt%, 30 wt% and even as great as a 40 wt% or as an aqueous salt slurry. The composition and salt solution or slurry should be mixed at a ratio sufficient to destabilize the composition to cause consolidation of the solids therein. In one aspect of the present disclosure, the composition and the salt solution are mixed at a ratio of between 5.0:1.0 and 1.0:5.0, e.g., mixed at a ratio between 1.5:1.0 to 1.0:1.5 composition to salt solution.
[0044] In some embodiments of the present processes, it can be more advantageous to use a natural source of a highly soluble salt or salts such as in a natural body of water including such salts in sufficiently high concentration such as at least about 2 wt% and even at least about 3 wt% or greater. For example, ocean or sea water can be used as a source of highly soluble salts, which can significantly improve the economics of the process under certain conditions. The vast majority of seawater has a salinity of between 31 g/kg and 38 g/kg, that is, 3.1-3.8%. On average, seawater in the world’s oceans has a salinity7 of about 3.5% (35 g/L, 599 mM). Seawater includes of a mixture of salts, containing not only sodium cations and chlorine anions (together totaling about 85% of the dissolved salts present), but also sulfate anions and calcium, potassium and magnesium cations. There are other ions present (such as bicarbonate), but these are the mam components. .Another natural source of highly soluble salts that can be used as a source of highly soluble salts includes a hypersaline body of water, e.g., a hypersaline lake, pond, or reservoir. A hypersaline body of water is a body of water that has a high concentration of sodium chloride and other highly soluble salts with saline levels surpassing ocean water, e.g., greater than 3.8 wt% and typically7 greater than about 10 wt%. Such hypersaline bodies of water are located on the surface of the earth and also subsurface, which can be brought to the surface as a result of ore mining operations.
[0045] After treating the aqueous fines with at least one highly7 water soluble salt the solids in the composition can be consolidated such as by mixing followed by gravity7 sedimentation in a settling tank or by centrifugation to increase the rate of forming a consolidated material in the treated composition. The consolidated material can be separated
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PCT/US2018/015423 from the process water by decanting, filtering, eletrofiltration, cross-flow filtering, vacuuming, and/or by mechanical dewatering, i.e., applying an external force to the consolidated material. Once separated, the consolidated material can be transferred for further dewatering or disposal.
[0046] Although highly water soluble salts can destabilize and consolidate solids in the aqueous fines, it was found that the process could be significantly improved by adding one or more polymer flocculant(s). The addition of a polymer flocculant to the highly water soluble salt significantly reduced the time for consolidation of fines. In addition, the processes of the present disclosure can also include treating aqueous fines with coarse particles, e.g., particles with sizes greater than 44 pm, such as sand, to significantly increase the solids content. Mixing with sand is appropriate for aqueous fines that have solids mostly as fines, as the fine particles can sit in the voids between the coarse particles, enhancing packing and solids content. It was found, however, that for certain compositions such as coal slurry, the addition of sand was not needed to achieve a high solids content, as there were sufficient coarse particles present in the aqueous fines stream to give a high solids content material.
[0047] Hence, implementations of the process of the present disclosure include, for example, (i) treating the composition with at least one highly water soluble salt to form a treated composition including a consolidated material in the process water, (ii) treating the composition with at least one highly water soluble salt and at least one polymer flocculant to form a treated composition including a consolidated material in the process water, (in) treating the composition with at least one highly water soluble salt and coarse particles to form a treated composition including a consolidated material in the process water, and (iv) treating the composition with at least one highly water soluble salt, at least one polymer flocculant and coarse particles to form a treated composition including a consolidated material in the process water. Each of these implementations can include aqueous solutions of the salt and/or polymer flocculant to treat the composition. Each of these implementations can include separating the process water from the consolidated material. Advantageously, the consolidated material has a density greater than the process water. The process water can then be readily separated from the consolidated material as, for example, by one or more of decanting, filtering, gravity7 draining, electrofiltering, crossflow filtering, vacuuming and other evaporating techniques, etc. and/or by one or more of a device for dewatering consolidated material such as a centrifuge, decanting centrifuge,
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PCT/US2018/015423 dewatering screw, hydrocyclone, vacuum belt filter, filter press or pressing devices, etc. In addition, the separated consolidated material can be disposed or deposited in a containment structure which allows removal of released water from the consolidated material.
[0048] Polymers that are useful in practicing the present disclosure include water soluble flocculating polymers such as polyacrylamides or copolymers thereof such as a nonionic polyacrylamide, an anionic polyacrylamide (APA.M) such as a polyacrylamide-co-acrylic acid, and a cationic polyacrylamide (CPAM), which can contain co-monomers such as acryloxyethyltrimethyl ammonium chloride, methacryloxyethyltrimethyl ammonium chloride, dime thy Idi ally ammonium chloride (DMDAAC), etc. Other water soluble flocculating polymers useful for practicing the present disclosure include a polyamine, such as a polvamine or quaternized form thereof, e.g., polyacrylamide-co-dimethylaminoethylacrylate in quatemized form, a polyethyleneimine, a polydiallyldimethyl ammonium chloride, a poly dicyandiamide, or their copolymers, a polyamide-co-amine, poly electrolytes such as a sulfonated polystyrenes can also be used. Other water soluble polymers such as polyethylene oxide and its copolymers can also be used. The polymer flocculants can be synthesized in the form of a variety of molecular weights (MW), electric charge types and charge density7 to suit specific requirements. Advantageously, the flocculating polymer used in practicing processes of the present disclosure do not include use of activated polysaccharides or activated starches, i.e., polysaccharides and starches that have been heat treated, in sufficient amounts to lower the density of the floc to below the density of the process water from which they are separated. Such activated polysaccharides and activated starches when used in sufficiently high dosages tend to form low density7 flocs which rise to the surface of an aqueous composition, which can hinder removal of solids in large scale operations involving high solids content and can also hinder dewatering of consolidated material.
[0049] The amount of polymer(s) used to treat aqueous fines should preferably7 be sufficient to flocculate the solids in the composition and any7 added coarse particles, e.g., sand. The amount of polymer(s) used to treat an aqueous composition which includes fines and process such as tailings can be characterized as a concentration based on the total weight of the composition or as a dosage based on the weight percent of the solids in the composition.
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PCT/US2018/015423 [0050] In some embodiments of the present disclosure, the concentration of the one or more polymer flocculant(s) in the treated composition has a polymer-composition concentration of no less than about 0.001 wt%, e.g., no less than about 0.003 wt%, 0.005 wt% or no less than about 0.01 wt%. For relatively short processing times, consolidation of the fines/sand mixture can be obtained at polymer-composition concentrations no less than about 0.04 wt%. The term “polymer-composition concentration” as used herein refers to the concentration of the flocculating polymer(s) in the treated composition and is determined by taking the percentage of the mass of the polymer(s) divided by the combined mass of the polymer(s) plus the compositi on and any water used to dissolve the polyraer(s). For example, combining 1 part undiluted (i.e., neat) polymer to 9999 parts tailings by weight results in a polymer-composition concentration of 0.01 wt%. Alternatively, treating tailings with an equal weight of a 0.02 wt% solution of the polymer also results in a polymer-composition concentration of 0.01 wt%. In certain embodiments, aqueous fines are treated with at least one polymer flocculant to yield a polymercomposition concentration of no less than about 0.02 wt%, such as no less than about 0.03 wt%, 0.04 wt%, 0.05 wt%, and even at least about 0.07 wt%, 0.09 wt%, 0.1 wt%, 0.2 wt%, etc. The amount of polymer flocculant can be used in greater concentrations. However, after certain high concentrations it becomes difficult to dissolve the flocculant, the solution becomes too viscous and the process is less economical.
[0051] In some embodiments of the present disclosure, the concentration of the one or more polymer flocculant(s) in the treated composition, e.g., tailings, has dosage (weight of the flocculant(s) to weight of the solids in the composition, e.g., tailings) of no less than about 0.005 wt%, e.g., no less than about 0.01 wt% and preferably no less than about 0.015 wt%, 0.020 wt%, 0.025 wt%, 0.03 wt%, or 0.04 wt%.
[0052] The amount of polymer flocculant can be reduced if the salt-composition concentration is increased. While the reason for this effect is not clear, a very low polymercomposition concentration of no less than about 0.001 wt%, e.g. no less than about 0.003 wt%, 0.005 wt%, 0.01 wt%, 0.02 wt%, 0.03 wt%, 0.04 wt%, 0.05 wt %, for example, can achieve reasonably fast consolidation of solids in composition, e.g., tailings, if the salt-composition concentration is increased.
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PCT/US2018/015423 [0053] Coarse particles useful for practicing certain processes according to the present disclosure are preferably sand and when used in treating compositions the amount of such particles are preferably in a sand to fines ratio (SFR ratio) of less than 4:1, e.g., between about 2.5:1.0 to about 0.5:1 or between about 2.25:1 to about 0.75:1. The SFR ratio is calculated by determining the amount of sand added to an estimated amount of solid fines m the aqueous fines on a weight basis. It is believed that the use of coarse particles facilitates packing of the consolidated fines which advantageously increases the solids content and can even form a jammed structure of consolidated solids, i.e. a structure in which generally individual particles of the consolidated solid can no longer move freely relative to other particles.
[0054] Treating an aqueous composition including fines and process water, e.g,, tailings, with at least one highly water soluble salt and optionally with either or both of at least one polymer flocculant and/or optionally sand can be carried out in a number of ways. In certain embodiments, treating the composition includes combining and/or mixing the various components. In addition, the at least one salt can be added directly to the composition either as an undiluted solid in powder form or as a solution; the at least one polymer flocculant can be added directly to the composition either as an undiluted material or as a solution, and the sand can be added to the composition directly or with the salt and/or polymer or solutions thereof. The salt and polymer can be combined in a single solution, with or without sand, and combined with the composition. The order of combining the salt, polymer and sand to the composition can give equivalent results and optimization of the process will depend on the type of composition, and the scale and equipment used in the process.
[0055] However, it tends to be more convenient to first prepare one or more solutions including the one or more highly water soluble salt(s) and the one or more polymer flocculant(s) followed by combining the one or more solutions with the composition and sand. In certain embodiments, an aqueous solution of one or more highly water soluble salt(s) can be prepared having a concentration of no less than about 0.5 wt% or 1 wt%, e.g., at least about 2 wt%, 3 wt%, 4 wt%, 5 wt%, 6 wt%, 7 wt%, 10 wl%, 20 wt%, 30 wt% and even as great as a 40 wt% or as an aqueous salt slurry for use in treating the composition. The one or more polymer flocculant(s) can also be included m the aqueous solution of the salt(s) and can have a concentration of no less than about 0.005 wt%, e.g., no less than about 0.01 wt%, 0.04 wt%, 0.05
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PCT/US2018/015423 wt %, 0.1 wt%, 0.2 wt%, 0.4 wt%, for example. The aqueous solution of the highly water soluble salt(s) and polymer flocculant(s) can be used to treat the composition and can be combined with such compositions at a ratio of between 5.0:1.0 and 1.0:5.0, e.g., at a ratio between 1.5:1.0 to 1.0:1.5 of composition to aqueous solution. Sand can be combined with the composition before, during, or after combining the composition with the solutions.
[0056] Because highly water soluble salts and polymer flocculants that are preferably water soluble are used m the process of the present disclosure, the temperature of the treated aqueous fines need not be elevated above ambient to practice the process. In certain embodiments, treating the composition according to the various embodiments herein can be carried out at a temperature of no more than 50 °C, e.g., no more than about 40 °C or about 30 °C. In other embodiments, such as oil sands froth tailings consolidation, the tailings stream may already be warm or hot as a result of prior processing. The processes of the present disclosure can be applied directly to these tailings streams.
[0057] In practicing aspects of the present disclosure, compositions, e.g., a suspension of particulate solids in an aqueous liquid which include fines and process water, can be consolidated by treating such compositions with at least one highly water soluble salt or aqueous solutions thereof and can optionally include either or both of at least one polymer flocculant, e.g., a water-soluble flocculating polymer, or aqueous solutions thereof, and/or optionally coarse particles, e.g., sand to form a treated composition. Treating compositions, e.g., tailings, in this manner can cause destabilization and consolidation of the solids, e.g., fines and sand, in the treated composition to form a consolidated material, which can settle under gravity’ relatively’ quickly, in the process water.
[0058] The treated compositions and/or consolidated material can be further dewatered to further separate the process water from the consolidated material and, in some instances, further consolidate the solids. In some embodiments, the consolidated material formed in the treated compositions can be separated from the process water by any one or more of decanting, filtering, e.g., electrofiltering, cross-flow filtering, gravity’ draining, vacuuming and other evaporating techniques, etc. and/or by any one or more of a mechanical dewatering, i.e., applying an external force to the consolidated material, with a device for dewatering consolidated material such as by applying a centrifuge, decanting centrifuge, dewatering screw, hydrocyclone, filter press,
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PCT/US2018/015423 pressing device, etc. or combinations thereof. In one aspect of the processes of the present disclosure, the process water can be separated from the consolidated material by passing a stream of treated composition through a cross-flow filter, e.g., a porous or slotted pipe, which filters and dewaters the treated composition stream to separate the process water from the consolidated material. The process water can then be readily separated from the consolidated material. In another aspect of the processes of the present disclosure, the process water can be separated from the consolidated material by gravity draining to achieve a solids content of at least about 70% within about a month after treating the tailings, e.g., within about two weeks or within about one week of gravity draining after treating the tailings. In still further aspect of the processes of the present disclosure, the consolidated material can be further dewatered after separating from the treated composition by depositing the separated consolidated material in a thin lift deposition.
[0059] The consolidated material formed in the treated compositions can advantageously have a high solids content, e.g., a solids content of greater than about 50% and at least about 60%, 65%, 70% and 75% by weight. In addition, the consolidated material formed in the treated compositions according to certain embodiments can result in a high solids content after mixing and/or dewatering the treated compositions in a short period. In embodiments of the present disclosure, the consolidated material can have a solids content of greater than about 50% and at least about 60%, 65%, 70%, 75% and 80% by weight after mixing and/or dewatering. In certain embodiments a solids content of at least about 70 % is achieved within about one month of gravity draining after treating the composition, e.g., within about two weeks or within about one week of gravity draining after treating the composition.
[0060] In an embodiment of the present disclosure, the process includes mixing the composition with a highly water soluble salt, e.g., an ammonium based salt, a water soluble polymer, e.g., a polyacrylamide, and optionally sand, such as in a sand to fines ratio of between about 2.25:1 to about 0.75:1 to form a treated composition including a consolidated material having a high solids content, e.g., a solids content of greater than about 50% by weight, e.g., at least about 60%, 65%, 70 wt% or higher in less than 10 minutes, depending on the dewatering method used.
[0061] Another advantage of the processes of the present disclosure is the recovery of materials from tailings that include rare earth elements. For example, certain tailings can include
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PCT/US2018/015423 valuable minerals that include rare earth elements. A rare earth element (REE), as defined by IUPAC, is one of a set of seventeen chemical elements in the periodic table, specifically the fifteen lanthanides, as well as scandium and yttrium. Scandium and yttrium are considered rare earth elements because they tend to occur in the same ore deposits as the lanthanides and exhibit similar chemical properties. Many of the REE are used in electronic devices, magnets, high performance coatings. Such REE include cerium (Ce), dysprosium (Dy), erbium (Er), europium (Eu), gadolinium (Gd), holmium (Ho), lanthanum (La), lutetium (Lu), neodymium (Nd), praseodymium (Pr), promethium (Pm), samarium (Sm), scandium (Sc), terbium (Tb), thulium (Era), ytterbium (Yb) and yttrium (Y).
[0062] REE in aqueous fines are typically in the form of an ion or oxide. For example, zirconium can be present as zircon, ZrSiCfi, titanium can be present as the minerals ilmenite, leucoxene and rutile. Coal ash and coal cleaning wastes contain rare earth elements. Fire clay coal ash has unusually high concentrations of Yttrium and zirconium. Oil sands tailings also contain REE.
[0063] The processes of the present disclosure are useful in recovering REE. It is believed that in some tailings, REEs absorb on the surface of clays in tailings. In other tailings, REEs are predominately included among the solids of the tailings but can also be in the process water. .Absorbed REEs can be exchanged with the highly water soluble salts of the present disclosure, e.g., ammonium based salts due to an exchange of ammonium ions for the REE ions. REEs from the solids of the tailings can be obtained by leaching the solids with acid followed by extraction and precipitation or by caustic decomposition followed by acid leaching.
[0064] Another aspect of processes of the present disclosure includes consolidating an aqueous composition including fines and process water, e.g., tailings, which include REE materials by treating the composition with at least one highly water soluble salt, e.g., an ammonium based salt such as ammonium sulfate, to form a treated composition including a consolidated material in process water which includes the REE materials in the process water and/or among the consolidated materials. In one aspect of the present disclosure, the treated composition consolidates the fines and also separates REE materials from the solids and into the process water. The process water can then be separated from the consolidated material and the REE materials can be recovered from the separated process water. The REE materials can be
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PCT/US2018/015423 recovered from the process water by precipitation, e.g., using oxalic acid, or extraction. Other methods for recovering REE from the process water include mineral processing and physical beneficiation, deep eutectic solvents/ionic liquids extraction, acid dissolution, high temperature phase separations, use of REE selective sorbents, photophoresis, in-situ brine injection and extraction, reactive grinding, etc. In other aspect of the present disclosure, the treated composition consolidates the fines and REEs are among the consolidated materials. The process water can then be separated from the consolidated material. The consolidated material can then be leached with acid, e.g., nitric acid, sulfuric acid, etc., followed by extraction with solvent and/or ion exchange resins and precipitated. Alternatively, the consolidated material can then be treated with a caustic reagent such as sodium hydroxide to decompose certain of the materials to form hydroxides of the REEs followed by leaching in acid, e.g., HC1.
[0065] In addition, the composition which includes REE materials can be treated with at least one polymer flocculant and optionally sand to form the treated composition. The treated composition can have a salt-composition concentration of at least 0.5 wt% of the at least one highly water soluble salt and preferably no less than about 1 wt%, such as at least about 2 wt% and even greater than about 3 4 wt%, 5 wt%, etc. of the at least one highly water soluble salt.
[0066] The process of the present disclosure allows for large scale treatment of aqueous fines in a continuous or semi-continuous process with further recovering, recycling and purifying at least a portion of the process water in the aqueous fines and optionally recovering REE materials. When non-hydrolyzing, highly water soluble salts are used in the processes of the present disclosure, the process water separated from an initial treated composition can advantageously include a significant amount of the one or more highly water soluble salt(s) initially used to treat the composition. In certain embodiments, the separated process water includes the at least one highly water soluble salt and the process includes recovering at least a portion of the separated process water; recycling at least a portion of the recovered separated process water to treat additional aqueous fines; and/or purifying at least a portion of the recovered process water. In other embodiments, the separated process water includes REE materials salt and the process further includes recovering at least a portion of the separated process water; recycling at least a portion of the recovered separated process water to treat
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PCT/US2018/015423 additional aqueous fines; recovering the REE materials and/or purifying at least a portion of the recovered process water.
[0067] Figure 1 schematically illustrates such an exemplary continuous or semicontinuous process. As shown in the figure, aqueous compositions including fines and process water are treated with one or more highly water soluble salt(s), and optionally one or more polymer flocculant(s) and optionally coarse particles (sand) by combining a stream of the salt(s) (101a), which can be an aqueous solution with a stream of the composition (103a). For this embodiment, the composition is a tailings composition but other aqueous fines compositions can be processed in the same manner. Optionally, the composition can also be treated with one or more polymer flocculant(s) by combining a stream of the flocculants(s) (102a), which can be as an aqueous solution, with the composition stream (103a). Alternatively, the salts(s) and flocculant(s) can be combined together as a solution to treat the tailings as a stream thereof. Coarse particles (sand) can also be added to the composition or stream thereof and/or to any or all of the solution streams, [0068] The solution streams of salt(s) and polymer(s) can be sourced from holding tanks
101 and 102 and the streams of aqueous fines and sand can be sourced from holding tanks 103 and 105, respectively. Alternatively, the Tailings can be sourced from an oil sands extraction operation.
[0069] For this embodiment, the stream of salt(s) (101a) and polymer(s) (102a) and tailings stream (103a) are carried to mixing device 107 where a stream of sand (105a) is added and the combination mixed. Mixing device 107 can be an inline mixer, a mixing tank, ribbon mixer or other mixing device that can mix streams 101a, 102a, 103a and 105a. For this embodiment, the aqueous fines are combined with the salt(s) and polymer(s) as solutions followed by addition of sand to treat the aqueous fines. However, the order can be changed, e.g., the sand can be combined with the aqueous fines (105b) followed by mixing with the salt(s) and polymer(s) solutions. The sand can be added as a wet or dry stream. In some embodiments, the combination of the streams in a line can cause sufficient mixing to eliminate the need for a separate mixing device, e.g., inline mixing, and the combined streams can be carried directly to a mechanical dewatering device to separate consolidated material from process water and, in some instances, to further consolidate the solids in the consolidated material.
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PCT/US2018/015423 ίο [0070] As shown in the embodiment of Figure 1, after mixer 107, the treated aqueous fines, which include a consolidated material and process water, is transferred to dewatering device 109 to separate the process water from the consolidated material. Such dewatering devices include, for example, one or more of a decanting, filtering, electrofiltering, cross-flow filtering, gravity draining, or vacuuming device or combination thereof and/or by one or more of a device for dewatering consolidated material such as a centrifuge, decanting centrifuge, dewatering screw, hydrocyclone, vacuum belt filter, filter press or pressing devices, etc. or combinations thereof.
[0071] Separated process water can be recovered and collected in tank 111 and separated consolidated material can be recovered and collected in container 113. For this embodiment, the recovered process water in tank 111 includes the process water from the aqueous fines, e.g., tailings, diluted with stream 101a and thus includes residual salt(s) from the one or more highly water soluble salt(s) and can possibly include residual polymer(s) from the one or more polymer flocculant(s) as well as contaminants from the aqueous fines. If the aqueous fines include REE materials, the recovered process water in tank 111 and/or the consolidated material in 113 can also include REE materials. There are also highly water soluble salts that are constituents of the original aqueous fines and these become part of the recovered process water. The recovered process water in tank 111 can then be transferred to a water purifying system 115 to purify at least a portion of the recovered process water which is transferred to tank 117. Water purifying systems that can be used for embodiments of the processes of the present disclosure include reverse osmosis systems, vacuum distillation systems, electrodialysis, filtration systems, etc. The remaining, non-purified recovered process water is transferred to tank 119 to recover process water including the one or more highly water soluble salt(s) and highly water soluble salts that are constituents of the original aqueous fines. This remaining, non-purified recovered process water can be recycled back to the treatment process. For this embodiment, at least a portion of the non-purified recovered process water can be recycled back to holding tank 101 and deficiency in the concentration of the salt(s) or polymer(s) can be corrected by adding additional highly water soluble salt(s) or polymer flocculant(s) from one or more make-up tanks such as make-up containers 121 and 122.
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PCT/US2018/015423 [0072] The process of the present disclosure can also include recovering REE materials from recycled separated process water or from the consolidated solids. The REE materials can be recovered from the process water by precipitation, e.g., using oxalic acid, or extraction. Other methods for recovering REE from the process water include mineral processing and physical beneficiation, deep eutectic solvents/ionic liquids extraction, acid dissolution, high temperature phase separations, use of REE selective sorbents, photophoresis, in-situ brine injection and extraction, reactive grinding, etc. The process of the present disclosure can also include recovering REE materials from the consolidated solids by acid leaching or caustic decomposition.
[0073] The process of the present disclosure can include adding an organic solvent (e.g., naphtha, kerosene or a C5-8 hydrocarbon, such as pentane, hexane, heptane, benzene, toluene, etc. or mixtures thereof) to dilute organic material included with the aqueous fines, e.g., tailings such as residual hydrocarbons, organic solvents, oil, bitumen. The addition of an organic solvent forms an organic mixture with the organic material which can be removed.
[0074] In addition, the consolidated solids can be recovered. The recovered consolidated solids can include residual highly water soluble salt(s) from the treatment of the tailings. When the salt used in treating the tailings are beneficial to plant life, such as an ammonium based salt or sulfate based salt or phosphate based salt, the residual salt can act as a fertilizer with the consolidated solids. The recovered consolidated solids can include REE materials which can be separated from the consolidated solids as explained elsewhere.
EXAMPLES [0075] The following examples are intended to further illustrate certain preferred embodiments of the invention and are not limiting in nature. Those skilled in the art will recognize, or be able to ascertain, using no more than routine experimentation, numerous equivalents to the specific substances and procedures described herein.
[0076] Coal Ash Slurry Consolidation [0077] An initial sample of a coal ash slurry' was analyzed by infrared spectroscopy to determine the content of solids content. Further, the sample was estimated to have 30% or more coal fines present, i.e., a mixture of fine coal particles and fine mineral particles. Approximately
WO 2018/144336
PCT/US2018/015423 g of the coal slurry was placed in a vial and an equal weight of an aqueous ionic solution was added and the diluted slurry shaken to mix the components. The ionic liquid was composed of water, 10 wt% ammonium sulfate and 0.1 wt% polyacrylamide (PAM). Settling started immediately, as can be seen in the picture on the left in Figure 2. The vial was then centrifuged for 30 seconds at 3000 rpm and the particles consolidated into a compact mass, as shown in the picture in the center of Figure 2. The supernatant liquid appeared to be clear, with no visible suspended particles. Upon removal of the liquid it was found that the compacted solids have enough cohesive strength to hold their shape when the vial was inverted, as can be seen in the picture on the right in Figure 2.
[0078] The material was removed from the vial (Figure 3, left) and a portion dried. The consolidated material had an initial solids content of 54%. Some of the remainder was pressed (by hand) between paper towels (Figure 3, right). This pressed material had a solids content of 74%.
[0079] Varying Salt and Salt Concentration in Treating Oil Sands Tailings [0080] Additional experiments were carried out with various highly water soluble salts and in different concentrations and with and without sand to treat oil sands tailings. A series of salt/polymer solutions were prepared. All of the salt/polymer solutions included 0.1 wt% of polyacry lamide (PAM) but varied the type and concentration of the salt. For example, a series of 10 wt%, 5 wt% and 2 wt% calcium chloride solutions each with 0.1 wt% of PAM were prepared and used to treat MFT. Other 10 wt%, 5 wt% and 2 wt% salt solutions of ammonium sulfate, potassium chloride, etc. were prepared each with 0.1 wt% of PAM. An equal weight of a particular salt/polymer solution was then combined with MFT, with or without sand, in a vial followed by vigorous mixing. The vials were then centrifuged at 3000 rpm on a LW Scientific laboratory' centrifuge for 30 seconds to form a consolidated material in the form of a slurry. After centrifugation, the supernatant liquid was separated from the consolidated material by a pipette. The consolidated material was then weighed, dried and reweighed to determine a solids content of the consolidated material. The various salts and their concentrations which were used to treat MFT and the resultant solids content data are summarized m Tables 1 and 2 below.
WO 2018/144336
PCT/US2018/015423
Table 1: Solids content of MET treated with an equal weight of a salt/PAM solution without the addition of sand and after centrifugation.
| Sait (+0.1 wt% PAM) No Sand | 10% Concentration1 | 2 5% Concentration | 2% Concentration3 |
| Ferric Chloride (FeCk) | 34.9% | „„ | 35.6% |
| Aluminum Sulfate (A12(SO4)3) | 33.1% | __ | 34.1% |
| Calcium Chloride (CaCl2) | 36.8% | 37.1% | 35.8% |
| Ammonium Sulfate (NH4SO4) | 33.1% | 31.8% | 31.4% |
| Potassium Chloride (KC1) | 35.4% | 32.4% | 33.5% |
Table 2: Solids content of MET treated with an equal weight of a salt/PAM solution with the addition of sand (SER ratio 1:1) after centrifugation.
| Salt (+0.1 wt% PAM) With Sand | 10% Concentration1 | 5% Concentration2 | , q 2% Concentration' |
| Ferric Chloride (FeCl3) | 45.7% | - | 52.8% |
| /Aluminum Sulfate (A12(SO4)3) | 51.4% | - | 53.7% |
| Calcium Chloride (CaCl2) | 58% | 56.8% | 56.1% |
| Ammonium Sulfate (NH4SO4) | 53.6% | 52.3% | 53.5% |
| Potassium Chloride (KC1) | 53.4% | 52.5% | 53.9% |
1. The salt-tailings concentration was about 5 wt%.
2. The salt-tailings concentration was about 2.5 wt%.
3. The salt-tailings concentration was about 1 wt%.
WO 2018/144336
PCT/US2018/015423 [0081] Table 1 reports the solids content of dried consolidated material following treating of MFT with the various salt/polymer solutions without sand. After centrifugation for just 30 seconds, the highly water soluble salts gave solids contents for the consolidated materials in a range between about 31%-37%. However, the use of highly water soluble salts having a multivalent cation such as the aluminum and ferric cations appeared to cause fouling of the vial walls and gave a less cohesive consolidated material as compared to highly water soluble salts having a monovalent cation under the tested conditions. In some tests using salt concentrations of 10%, the clarified water sitting on top of the consolidated materials were removed using a pipette and the wet solids pressed between paper towels. It was found that the salts with multivalent cations, aluminum chloride (AlCfi), ferric chloride (FeCfi) and calcium chloride (CaCh), which all gave significant deposits of a slimy material on the vial walls, were less cohesive than the pressed solids obtained using salts with monovalent cations, such as the ammonium salts NH4CI and (NTLfoSO;.
[0082] Table 2 reports the solids content of dried consolidated material following treating
MFT with the various salt/polymer solutions and sand. Sand was added with a 1:1 sand to fines ratio (i.e., 1.5 g of sand was added to the 5 gm of MFT having 30% solids to give a 1:1 ratio of the weight of sand to that of the solids in the MFT). After centrifugation for just 30 seconds, the highly water soluble salts gave solids contents for the consolidated materials in a range between about 46%-58%, which was significantly higher than the range of solids contents without use of sand. Although the solids content of the vials containing added sand is twice those without sand, the volume of the centrifuged slurry' is about the same.
[0083] The data in Tables 1 and 2 show that addition of 2 wt% salt solution to treat MFT was as effective as a 10 wt% salt solution. That is, a 1 wt% salt-tailings concentration was as effective as a 5 wt% salt-tailings concentration. Since an equal weight of the salt/polymer solution was used to treat MFT, the salt concentration of the added salt in the treated tailings is one-half of the concentration in the salt/'polymer solution, i.e., the added 2 wt% salt solution provided a 1 wt% salt-tailings concentration and the 10 wt% salt solution provided a 5 wt% salttailings concentration. The salt-tailings concentration in treated MFT can be achieved in a number of ways. For ease of handling in the foregoing vial tests, it was convenient to combine equal weights of salt/polymer solutions to MFT. However, smaller amounts of salt/polymer
WO 2018/144336
PCT/US2018/015423 solutions with higher concentrations thereof to give the same salt-tailings concentration give equivalent results of consolidated materials.
[0084] Centrifuging in flat-bottomed vials is not as effective in terms of producing a high solids material as using centrifuge tubes. It should be kept in mind that for all sets of laboratory vial and tube tests, there is always solution remaining in the voids between the particles. It will be shown later that the solids content of the consolidated material can easily be increased from the 46%-58% range by simply draining or the use of mechanical dewatering methods known to the art, such as filter presses, belt filters, cross-flow filtering, dewatering sand screws, decanting centrifuges, hydrocyclones, etc.
[0085] Varying Salt Concentration and Polymer Concentration in Treating Oil Sands
Tailings [0086] When salt, polymer and sand are used together, salt-tailings concentrations in excess of 0.5 wt% and preferably no less than about 1% should be used to achieve reasonably fast consolidation of the solids in the tailings. In addition, although a degree of consolidation of the fines/sand mixture is obtained at polymer-tailings concentrations as low as 0.01 wt% for relatively short processing times, superior results are obtained at polymer-tailings concentrations of 0.05% and higher. These preferences were determined by a set of vial experiments. The top set of vials in Figure 4 shows results obtained by adding 5 g of a 2 wt% ammonium sulfate ((NH4)2SO4) solution containing PAM to 5 g of MFT. Sand was also added to give a sand-tofines ratio of 1:1 (i.e., 1.5 g of sand was added). The amount of PAM in the solutions was varied between 0.1% (by weight) and 0.02% (by weight). The bottom set of vials show what is observed when a 1 wt% of the ammonium sulfate was used. The vials were centrifuged at 3000 rpm for 30 seconds to accelerate settling.
[0087] It can be seen that for all the vials treated with the 1 wt% (NH4)2SO4 solutions, there is a degree of settling of the fines and sand, but the supernatant liquid contains a significant amount of suspended particles. In addition, visually there appears to be a degree of segregation of the sand and fines. In contrast, the MFT treated with a 2 wt% (NH4)2SO4 solution containing 0.1 wt% PAM showed settled and compacted solids in contact with a clear supernatant. As the amount of polymer in the solution is reduced from vial A4 to E4, the clarity of the supernatant decreases, as more suspended particles remain in the liquid phase. Greater clarity of the
WO 2018/144336
PCT/US2018/015423 supernatant liquid should be achievable at longer centrifuge times, but for short processing times, treating MFT to result in a salt-tailings concentration of no less than about 0.5 wt% and a polymer-tailings concentration of no less than about 0.04 wt% are preferable.
[0088] The solids contents of the consolidated materials in each of the vials shown in
Figure 4 was determined by drying, i.e., the centrifuged consolidated material was separated from its supernatant liquid, the wet mass weighed, dried and reweighed to determine a solids content. The solids content of the consolidated materials for the sets of vials are summarized in Table 3.
Table 3: The solids content of centrifuged ammonium sulfate/PAM treated MFT as determined by separating and drying consolidated material.
| 0.1% PAM | 0.08% PAM | 0.06% PAM | 0.04% PAM | 0.02% PAM | |
| % Solids | % Solids | % Solids | % Solids | % Solids | |
| 2% (NH4)2SO4 | 60.3% | 58.8% | 58.1% | 52.0% | 48.5% i |
| 1% (NH4)2SO4 | 54.4% | 57.2% | 58.1% | 56.3% | 44.6% : |
[0089] It can be seen that for the 2 wt% (NH^SOq solution containing 0.1 wt% PAM, a solids content of just over 60% was achieved. This decreased only slightly when treating MFT with solutions including PAM concentrations of 0.08 wt% and 0.06 wt%, but significantly at lower PAM concentrated solutions. Treating MFT with an equal weight of the (NH4)2SO4 / polymer solutions resulted in a salt-tailings concentration of about 1 wi% for each of vials A4E4, and for vial A4, a polymer-tailings concentration of about 0.05 wt% PAM, for vial B4 a polymer-tailings concentration of about 0.04 wt% PAM, for vial C4 a polymer-tailings concentration of about 0.03 wt% PAM, for vial D4 a polymer-tailings concentration of about 0.02 wt% PAM, and for vial E4 a polymer-tailings concentration of about 0.01% PAM. For the 1 wt% (NH4)2SO4 solutions, the solids content was very variable, reflecting the problems with segregation of coarse and fine particles in the consolidated materials in these experiments.
[0090] Increased Salt Concentration .Allows for Lower Polymer Concentration
WO 2018/144336
PCT/US2018/015423 [0091] When salt, polymer and sand are used together to treat tailings, it was observed that the polymer-tailings concentration can be reduced if the salt-tailings concentration is increased under certain circumstances. Thus, very low polymer-tailings concentration can achieve reasonably fast consolidation of solids in the tailings if the salt-tailings concentration is increased. Figure 5 illustrates that as the salt concentration increases, less polymer flocculant is needed to obtain clear supernatant solutions. For these tests, the polymer-tailings concentration increases from 0.01% to 0.05% in 0.01% increments from right to left while the salt-tailings concentration increases from 1% to 2% from top to bottom.
[0092] Varying Polymer Concentration in Treating Oil Sands Tailings with Seawater [0093] For these experiments, solutions of seawater (sourced from the U.S. eastern shore of the Atlantic Ocean) were prepared with various concentrations of a nonionic polyacrylamide (available from SNF as FA920) between 0.1% (by weight) and 0.02% (by weight). The concentration of highly soluble salts in the seawater is believed to be greater than 3 wt%. The seawater-polymer solutions were used to treat MFT from oil sands processing. An equal amount of seawater -polymer solution was used to treat MFT (about 5 g of seawater -polymer solution to about 5 g of MFT) in a vial. The treated mixtures were first stirred and then the vials were centrifuged at 3000 rpm for 30 seconds to accelerate settling. The results are shown in the picture of Figure 6. From left to right, the seawater used to treat the MFT included about 0.1 wt%, 0.08 wt%, 0.06 wt%, 0.04 wt% and 0.02 wt% of the polymer flocculant, respectively. These experiments show that a mixture of highly soluble salts sourced from an ocean can be used in the process of the present disclosure.
[0094] Only the preferred embodiment of the present invention and examples of its versatility are shown and described in the present disclosure. It is to be understood that the present invention is capable of use in various other combinations and environments and is capable of changes or modifications within the scope of the inventive concept as expressed herein. Thus, for example, those skilled in the art will recognize, or be able to ascertain, using no more than routine experimentation, numerous equivalents to the specific substances, procedures and arrangements described herein. Such equivalents are considered to be within the scope of this invention, and are covered by the following claims.
Claims (33)
- WHAT IS CLAIMED IS:1. A process of consolidating an aqueous composition which includes fines and process water, the process comprising:treating the composition with at least one highly water soluble salt to form a treated composition including a consolidated material in the process water; and separating the process water from the consolidated material.
- 2. A process of consolidating an aqueous composition which includes fines and process water, the process comprising:treating the composition with at least one highly water soluble salt and at least one polymer flocculant to form a treated composition including a consolidated material in the process water; and separating the process water from the consolidated material.
- 3. A process of consolidating an aqueous composition which includes fines and process water, the process comprising:treating the composition with at least one highly water soluble salt and coarse particles to form a treated composition including a consolidated material in the process water; and separating the process water from the consolidated material.
- 4. A process of consolidating an aqueous composition which includes fines and process water, the process comprising:treating the composition with at least one highly water soluble salt, at least one polymer flocculant and coarse particles to form a treated composition including a consolidated material in the process water; and separating the process water from the consolidated material.
- 5.The process of any one of claims 1-4, wherein the composition is tailings.WO 2018/144336PCT/US2018/015423
- 6. The process of any one of claims 1-4, wherein the at least one highly water soluble salt is a non-hydrolyzing salt.
- 7. The process of any one of claims 1-4, wherein the at least one highly water soluble salt has a solubility in water of greater than 10 g/100 g at 20 °C
- 8. The process of any one of claims 1-4, wherein the at least one highly water soluble salt has a monovalent cation.
- 9. The process of any one of claims 1-4, wherein the treated composition has a saltcomposition concentration of the at least one highly water soluble salt of at least 0.5 wt%.
- 10. The process of any one of claims 1-4, wherein the at least one highly water soluble salt is an ammonium based salt.
- 11. The process of claim 10, wherein the ammonium based salt is selected from ammonium chloride, ammonium bromide, ammonium carbonate, ammonium bicarbonate, ammonium nitrate, ammonium sulfate, ammonium phosphate, or a combination thereof.
- 12. The process of any one of claims 2 or 4, wherein the at least one polymer flocculant is a polyacrylamide or co~polymer thereof.
- 13. The process of any one of claims 2 or 4, the treated composition has a polymercomposition concentration of the at least one polymer flocculant of no less than about 0.04 wt%.
- 14. The process of any one of claims 3 or 4, wherein the composition is treated with sand at a sand to fines ratio between 2.5:1.0 to 0.5:1.WO 2018/144336PCT/US2018/015423
- 15. The process of any one of claims 1-4, wherein treating the composition includes combining a stream of the composition with a stream of an aqueous solution including the at least one highly water soluble salt to produce a treated composition stream.
- 16. The process of any one of claims 2 or 4, wherein treating the composition includes combining a stream of the composition with a solution including the at least one highly water soluble salt and the at least one polymer flocculant to produce a treated composition stream.
- 17. The process of any one of claims 2 or 4, wherein treating the composition includes combining a stream of the composition with a stream of an aqueous solution including the at least one highly water soluble salt and a stream of an aqueous solution including the at least one polymer flocculant to produce a treated composition stream.
- 18. The process of claim 4, wherein treating the composition includes combining a stream of the composition with a stream of an aqueous solution including the at least one highly water soluble salt and a stream of an aqueous solution including the at least one polymer flocculant and adding sand to the composition and/or to at least one of the streams to produce a treated composition stream.
- 19. The process of claim 15, wherein the streams are mixed in line and optionally with an inline mixer to produce the treated composition stream.
- 20. The process of claim 15, wherein the treated composition stream is passed through a cross-flow filter to separate the process water from the consolidated material.
- 21. The process of any one of claims 1-4, comprising separating the process water from the consolidated material by any one or more of decanting, filtering, vacuuming, gravity draining, or combinations thereof.WO 2018/144336PCT/US2018/015423
- 22 The process of any one of claims 1 -4, wherein separating the process water from the consolidated material includes mechanically dewatering the consolidated material.
- 23. The process of any one of claims 1-4, wherein separating the process water from the consolidated material includes gravity draining to further dewater the consolidated material.
- 24. The process of any one of claims 1-4, wherein the consolidated material has a solids content of at least 45% by weight.
- 25. The process of any one of claims 1-4, further comprising recovering at least a portion of the separated process water.
- 26. The process of claim 25, further comprising recycling at least a portion of the recovered separated process water to treat additional compositions.
- 27. The process of claim 25, further comprising purifying at least a portion of the recovered process water.
- 28. The process of any one of claims 1-4 wherein the composition includes rare earth elements (REE) and treating the composition with at least one highly water soluble salt forms a treated composition including REE in the process water and/or in the consolidated materials.
- 29. The process of claims 28, further comprising separating the process water from the consolidated material; and recovering the REE from the separated process water.
- 30. The process of claims 28, further comprising separating the process water from the consolidated material; and recovering the REE from the consolidated materials.WO 2018/144336PCT/US2018/015423
- 31. The process of claims 28, further comprising separating the process water from the consolidated material; and recovering the REE from the separated process water and the consolidated materials.
- 32. The consolidated material obtained from any one of claims 1-4.
- 33. The consolidated material obtained from claim 28.
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| US10913670B2 (en) | 2016-05-05 | 2021-02-09 | Extrakt Process Solutions, Llc | Oil sands tailings treatment |
| WO2020172265A1 (en) * | 2019-02-19 | 2020-08-27 | Extrakt Process Solutions, Llc | Water management system for ore mining operation |
| AU2021253594A1 (en) * | 2020-04-09 | 2022-11-24 | Extrakt Process Solutions, Llc | Water management system for ore mining operation |
| CN113094880B (en) * | 2021-03-29 | 2023-03-31 | 广州中国科学院先进技术研究所 | Membrane distillation material concentration dynamic energy consumption calculation method, electronic equipment and computer readable storage medium |
| CN114011589B (en) * | 2021-11-01 | 2023-12-19 | 安徽汉华工贸有限责任公司 | Coal slime water treatment process based on dimethyl diallyl ammonium chloride and polyacrylamide |
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| US4270609A (en) * | 1979-09-12 | 1981-06-02 | Choules G Lew | Tar sand extraction process |
| US4376693A (en) * | 1981-07-13 | 1983-03-15 | Phillips Petroleum Company | Solid liquid extraction |
| CN1032744C (en) * | 1990-10-12 | 1996-09-11 | 周连海 | Method for clarifying tailing water |
| CN102596351B (en) * | 2009-09-15 | 2015-07-29 | 顺科能源公司 | To the method that the thin mine tailing of oil-sand slaking flocculates and dewaters |
| AU2013212579B2 (en) * | 2012-01-25 | 2016-05-26 | Basf Se | Method for dispersing and aggregating components of mineral slurries |
| CA2917534C (en) * | 2012-06-21 | 2020-03-10 | Suncor Energy Inc. | Dispersion and conditioning techniques for thick fine tailings dewatering operations |
| WO2013188982A1 (en) * | 2012-06-21 | 2013-12-27 | Suncor Energy Inc. | Enhanced techniques for dewatering thick fine tailings |
| US9067247B2 (en) * | 2012-07-06 | 2015-06-30 | The Chemours Company Fc, Llc | Treatment of tailings with deionized silicate solutions |
| CA2831352C (en) * | 2012-10-28 | 2017-01-10 | Syncrude Canada Ltd. | Co-processing of fluid fine tailings and fresh oil sands tailings |
| CN103308434B (en) * | 2013-05-20 | 2015-03-11 | 辽宁工程技术大学 | Muddy water infiltration experiment device |
| US10138427B2 (en) * | 2016-06-22 | 2018-11-27 | Extrakt Process Solutions, Llc | Separation of hydrocarbons from particulate matter using salt and polymer |
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