CN107815541A - The Fe loaded in hydrofluoric acid back extraction P204 organic phases3+And the method for strip liquor processing - Google Patents
The Fe loaded in hydrofluoric acid back extraction P204 organic phases3+And the method for strip liquor processing Download PDFInfo
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- KRHYYFGTRYWZRS-UHFFFAOYSA-N Fluorane Chemical compound F KRHYYFGTRYWZRS-UHFFFAOYSA-N 0.000 title claims abstract description 81
- 238000000034 method Methods 0.000 title claims abstract description 49
- 238000000605 extraction Methods 0.000 title claims abstract description 29
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 237
- 229910052742 iron Inorganic materials 0.000 claims abstract description 102
- 239000012074 organic phase Substances 0.000 claims abstract description 70
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 34
- 238000005406 washing Methods 0.000 claims abstract description 19
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims abstract description 17
- 235000011941 Tilia x europaea Nutrition 0.000 claims abstract description 17
- 239000004571 lime Substances 0.000 claims abstract description 17
- 239000002002 slurry Substances 0.000 claims abstract description 14
- 239000002893 slag Substances 0.000 claims abstract description 9
- 238000001556 precipitation Methods 0.000 claims description 22
- 239000007791 liquid phase Substances 0.000 claims description 8
- 229910000863 Ferronickel Inorganic materials 0.000 claims description 7
- 239000007790 solid phase Substances 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- 239000008367 deionised water Substances 0.000 claims description 4
- 229910021641 deionized water Inorganic materials 0.000 claims description 4
- 238000001914 filtration Methods 0.000 claims description 2
- 238000006386 neutralization reaction Methods 0.000 claims description 2
- 238000011001 backwashing Methods 0.000 claims 3
- 239000006210 lotion Substances 0.000 claims 2
- 238000003672 processing method Methods 0.000 claims 2
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 claims 1
- 238000003723 Smelting Methods 0.000 claims 1
- 235000014413 iron hydroxide Nutrition 0.000 claims 1
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 claims 1
- 239000013589 supplement Substances 0.000 claims 1
- 239000002699 waste material Substances 0.000 abstract description 13
- 239000007788 liquid Substances 0.000 abstract description 12
- WUKWITHWXAAZEY-UHFFFAOYSA-L calcium difluoride Chemical compound [F-].[F-].[Ca+2] WUKWITHWXAAZEY-UHFFFAOYSA-L 0.000 abstract description 8
- 229910001634 calcium fluoride Inorganic materials 0.000 abstract description 8
- 229960004887 ferric hydroxide Drugs 0.000 abstract description 8
- IEECXTSVVFWGSE-UHFFFAOYSA-M iron(3+);oxygen(2-);hydroxide Chemical compound [OH-].[O-2].[Fe+3] IEECXTSVVFWGSE-UHFFFAOYSA-M 0.000 abstract description 8
- 238000009853 pyrometallurgy Methods 0.000 abstract description 7
- 230000000694 effects Effects 0.000 abstract description 4
- 238000009854 hydrometallurgy Methods 0.000 abstract description 3
- 230000001502 supplementing effect Effects 0.000 abstract description 3
- UGKDIUIOSMUOAW-UHFFFAOYSA-N iron nickel Chemical compound [Fe].[Ni] UGKDIUIOSMUOAW-UHFFFAOYSA-N 0.000 abstract 1
- 239000000243 solution Substances 0.000 description 43
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical group Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 34
- 239000002253 acid Substances 0.000 description 12
- 238000004064 recycling Methods 0.000 description 11
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 9
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 238000000926 separation method Methods 0.000 description 9
- 239000002244 precipitate Substances 0.000 description 7
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 6
- 230000035484 reaction time Effects 0.000 description 6
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 4
- 238000011068 loading method Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000007787 solid Substances 0.000 description 4
- 230000009469 supplementation Effects 0.000 description 4
- 239000003513 alkali Substances 0.000 description 3
- 239000008346 aqueous phase Substances 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- -1 ferrous metals Chemical class 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 235000006408 oxalic acid Nutrition 0.000 description 3
- 239000012071 phase Substances 0.000 description 3
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 description 2
- WTDHULULXKLSOZ-UHFFFAOYSA-N Hydroxylamine hydrochloride Chemical compound Cl.ON WTDHULULXKLSOZ-UHFFFAOYSA-N 0.000 description 2
- 229910017855 NH 4 F Inorganic materials 0.000 description 2
- 229910017052 cobalt Inorganic materials 0.000 description 2
- 239000010941 cobalt Substances 0.000 description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 2
- 239000003085 diluting agent Substances 0.000 description 2
- 239000011737 fluorine Substances 0.000 description 2
- 229910052731 fluorine Inorganic materials 0.000 description 2
- 239000003350 kerosene Substances 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
- 239000003595 mist Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- 238000005554 pickling Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- LJKDOMVGKKPJBH-UHFFFAOYSA-N 2-ethylhexyl dihydrogen phosphate Chemical compound CCCCC(CC)COP(O)(O)=O LJKDOMVGKKPJBH-UHFFFAOYSA-N 0.000 description 1
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 229910000013 Ammonium bicarbonate Inorganic materials 0.000 description 1
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 229910001514 alkali metal chloride Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 229910001617 alkaline earth metal chloride Inorganic materials 0.000 description 1
- 235000012538 ammonium bicarbonate Nutrition 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000011114 ammonium hydroxide Nutrition 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 238000005352 clarification Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000010668 complexation reaction Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000004945 emulsification Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229940062993 ferrous oxalate Drugs 0.000 description 1
- 229910052738 indium Inorganic materials 0.000 description 1
- APFVFJFRJDLVQX-UHFFFAOYSA-N indium atom Chemical compound [In] APFVFJFRJDLVQX-UHFFFAOYSA-N 0.000 description 1
- OWZIYWAUNZMLRT-UHFFFAOYSA-L iron(2+);oxalate Chemical compound [Fe+2].[O-]C(=O)C([O-])=O OWZIYWAUNZMLRT-UHFFFAOYSA-L 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
- FBAFATDZDUQKNH-UHFFFAOYSA-N iron;hydrochloride Chemical compound Cl.[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-N 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 238000006303 photolysis reaction Methods 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 239000002243 precursor Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 229910052761 rare earth metal Inorganic materials 0.000 description 1
- 150000002910 rare earth metals Chemical class 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000012279 sodium borohydride Substances 0.000 description 1
- 229910000033 sodium borohydride Inorganic materials 0.000 description 1
- ISIJQEHRDSCQIU-UHFFFAOYSA-N tert-butyl 2,7-diazaspiro[4.5]decane-7-carboxylate Chemical compound C1N(C(=O)OC(C)(C)C)CCCC11CNCC1 ISIJQEHRDSCQIU-UHFFFAOYSA-N 0.000 description 1
- 229910001868 water Inorganic materials 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/20—Treatment or purification of solutions, e.g. obtained by leaching
- C22B3/26—Treatment or purification of solutions, e.g. obtained by leaching by liquid-liquid extraction using organic compounds
- C22B3/38—Treatment or purification of solutions, e.g. obtained by leaching by liquid-liquid extraction using organic compounds containing phosphorus
- C22B3/384—Pentavalent phosphorus oxyacids, esters thereof
- C22B3/3846—Phosphoric acid, e.g. (O)P(OH)3
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Geochemistry & Mineralogy (AREA)
- Geology (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明涉及一种氢氟酸反萃P204有机相中负载的Fe3+及反萃液处理的方法,属于湿法冶金技术领域。采用氢氟酸溶液反萃负载Fe3+的P204有机相,富铁反萃液采用石灰浆中和沉淀除铁、除F‑,所得到的贫铁反萃液直接返回系统洗涤反萃除铁后P204有机相,或者经补充氢氟酸后继续返回反萃工序使用,沉淀渣的成分为氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用。本方法在降低反萃成本的同时,达到无废渣、废液排放的效果,绿色环保,零排放。
The invention relates to a method for back-extracting Fe 3+ loaded in P204 organic phase with hydrofluoric acid and treating the back-extraction solution, and belongs to the technical field of hydrometallurgy. The P204 organic phase loaded with Fe 3+ is back-extracted with hydrofluoric acid solution, and the iron-rich back-extraction solution is neutralized and precipitated with lime slurry to remove iron and F ‑ , and the obtained iron-poor back-extraction solution is directly returned to the system for washing and back-extraction to remove iron The final P204 organic phase, or continue to return to the stripping process after supplementing with hydrofluoric acid, and the components of the precipitated slag are ferric hydroxide and calcium fluoride, which are recycled as slagging agents in the nickel-iron pyrometallurgy process. The method achieves the effect of no waste residue and waste liquid discharge while reducing the cost of stripping, and is environmentally friendly and zero discharge.
Description
技术领域technical field
本发明涉及一种氢氟酸反萃P204有机相中负载的Fe3+及反萃液处理的方法,属于湿法冶金技术领域。The invention relates to a method for back-extracting Fe 3+ loaded in P204 organic phase with hydrofluoric acid and treating the back-extraction liquid, and belongs to the technical field of hydrometallurgy.
背景技术Background technique
P204是一种酸性磷型萃取剂,中文名称二(2-乙基己基)磷酸,在有色金属的湿法冶金中获得广泛应用,如镍钴分离、萃取提锌、萃取提铟、镍、钴精炼流程中萃取除杂以及稀土萃取分组等。P204 is an acidic phosphorus-type extractant, the Chinese name is two (2-ethylhexyl) phosphoric acid, and it is widely used in the hydrometallurgy of non-ferrous metals, such as the separation of nickel and cobalt, extraction of zinc, extraction of indium, nickel, cobalt Extraction and removal of impurities and rare earth extraction and grouping in the refining process.
在使用P204萃取提取、分离金属或萃取除杂过程中,水相料液中不可避免存在部分铁离子杂质,P204萃取Fe(III)的能力较强,并且在各典型萃取工艺流程的实际反萃条件下有机相中的Fe(III)很难被完全反萃,因此,在P204有机相循环使用过程中会造成Fe(III)在有机相中的富集,并进而造成P204有机相萃取、分离能力下降;在工业应用时也有人将之称之为P204有机相“中毒”;为此,如何从负载Fe(III)的P204有机相中反萃除铁历来为人所关注。In the process of using P204 for extraction, separation of metals, or extraction and removal of impurities, some iron ion impurities are unavoidable in the aqueous phase feed liquid, and P204 has a strong ability to extract Fe(III). Fe(III) in the organic phase is difficult to be completely back-extracted under certain conditions. Therefore, during the recycling of the P204 organic phase, Fe(III) will be enriched in the organic phase, and then the P204 organic phase will be extracted and separated. The ability is reduced; in industrial applications, some people call it "poisoning" of the P204 organic phase; for this reason, how to strip and remove iron from the P204 organic phase loaded with Fe(III) has always been concerned.
由于Fe(III)在P204有机相中稳定性较强,即使采用高浓度的硫酸也无法有效反萃,目前,工业上最常采用的反萃剂为浓度约6mol/L的盐酸溶液,也有在盐酸溶液中加入碱金属或碱土金属氯化物进行反萃铁的工业应用;采用6mol/L左右的盐酸溶液或盐酸与氯化物混合溶液进行反萃的主要缺点是反萃剂酸雾大,操作条件恶劣;另外,反萃剂中的盐酸一般远远过量,在循环使用过程中反萃液中铁离子浓度逐渐上升,游离酸度下降,当游离盐酸浓度下降至5mol/L左右时其反萃铁的效果明显降低,只能作为废酸排放,重新更换新的反萃剂;此种情形操作造成反萃剂消耗量大,废酸中大量的游离盐酸未得到充分利用,而且废酸的中和处理又会带来大量的中和废渣,易污染环境。Due to the strong stability of Fe(III) in the P204 organic phase, it cannot be effectively stripped even with high-concentration sulfuric acid. At present, the most commonly used stripping agent in industry is hydrochloric acid solution with a concentration of about 6mol/L, and it is also available in The industrial application of adding alkali metal or alkaline earth metal chloride to the hydrochloric acid solution to strip iron; the main disadvantage of using a hydrochloric acid solution of about 6mol/L or a mixed solution of hydrochloric acid and chloride for stripping is that the stripping agent has a large acid mist and the operating conditions Poor; in addition, the hydrochloric acid in the stripping agent is generally far excessive. During the recycling process, the iron ion concentration in the stripping solution gradually increases, and the free acidity decreases. When the free hydrochloric acid concentration drops to about 5mol/L, the effect of stripping iron It can only be discharged as waste acid and replaced with a new stripping agent; in this case, the consumption of stripping agent is large, and a large amount of free hydrochloric acid in the waste acid is not fully utilized, and the neutralization of the waste acid is difficult. It will bring a large amount of neutralized waste residue, which is easy to pollute the environment.
鉴于此,申请号为200610152788.3的专利申请提出经盐酸再生后的P204中加入NaOH溶液,使P204有机中的Fe3+形成Fe(OH)3,经沉淀后,弃去沉降物Fe(OH)3,使含铁P204再生;该方法仍使用高浓度的盐酸再生,之后再使用氢氧化钠深度再生,过程中有Fe(OH)3沉淀生成,易出现乳化和三相物,两相分离困难,不利用再生操作。In view of this, the patent application No. 200610152788.3 proposes to add NaOH solution in the P204 regenerated by hydrochloric acid, so that the Fe in the P204 organically forms Fe( OH ) 3 , and after precipitation, the sediment Fe(OH) 3 is discarded , to regenerate iron-containing P204; this method still uses high-concentration hydrochloric acid for regeneration, and then uses sodium hydroxide for deep regeneration. During the process, Fe(OH) 3 is precipitated, which is prone to emulsification and three-phase matter, and it is difficult to separate the two phases. No regenerative operation is utilized.
申请号为201210036114.2的专利申请提出P204有机相先经6mol/L盐酸反萃再生,再经过氢氧化钠+碳酸氢铵的水溶液碱洗、草酸+硫酸的水溶液酸洗,整个过程仍无法摆脱6mol/L盐酸反萃剂的使用,含铁的盐酸废液处理困难,并且在6mol/L盐酸反萃处理后,再附加一段碱洗、一段酸洗,整体过程酸碱消耗大,废酸废碱的后续处理困难。The patent application with the application number 201210036114.2 proposes that the P204 organic phase is first regenerated by back extraction with 6mol/L hydrochloric acid, and then undergoes alkaline washing with aqueous solution of sodium hydroxide + ammonium bicarbonate, and pickling with aqueous solution of oxalic acid + sulfuric acid. The whole process still cannot get rid of the 6mol/L With the use of L hydrochloric acid stripping agent, it is difficult to treat the iron-containing hydrochloric acid waste liquid, and after the 6mol/L hydrochloric acid stripping treatment, an additional stage of alkali washing and a stage of pickling are added. The overall process consumes a lot of acid and alkali, and the cost of waste acid and alkali Subsequent processing is difficult.
专利号为93111639.2的专利采用2~4mol/L的NH4F做反萃剂,将反萃铁工序得到的(NH4)3FeF6加氨水调节pH至7~9,使之转化为Fe(OH)3沉淀,同时使NH4F再生返回使用;其缺点之一是反萃过程中生成(NH4)3FeF6沉淀,对反萃操作带来不便影响;另外,过程中使用含F试剂易对环境产生氟危害,如Fe(OH)3沉淀夹带含氟溶液易污染环境。Patent No. 93111639.2 uses 2-4mol/L NH 4 F as the stripping agent, and adds ammonia water to the (NH 4 ) 3 FeF 6 obtained in the iron stripping process to adjust the pH to 7-9 to convert it into Fe( OH) 3 precipitation, while NH 4 F is regenerated and returned to use; one of its disadvantages is that (NH 4 ) 3 FeF 6 precipitates are generated during the stripping process, which brings inconvenience to the stripping operation; in addition, the use of F-containing reagents in the process It is easy to cause fluorine hazards to the environment, such as Fe(OH) 3 precipitation entraining fluorine-containing solution is easy to pollute the environment.
申请号为201210164356.X的专利申请公开了一种洗脱P204萃取剂中Fe3+的方法;该方法基于Fe2+与P204萃取剂反应所生成的配合物的稳定性低于Fe3+这一原理,通过加入还原性试剂的方法,达到洗脱中毒萃取剂中Fe3+的目的,所采用的工艺原理实质上为还原反萃;其还原反萃温度为60~90℃,所用的还原剂为硼氢化钠、亚磷酸、盐酸羟胺或草酸,还原反萃时间0.5~2小时;由于还原反萃方法本身的限制,必须采用较高的反萃温度,不可避免会造成有机相的挥发损失,也未给出含铁废酸的处理方法。The patent application with the application number 201210164356.X discloses a method for eluting Fe in the P204 extractant; the method is based on the stability of the complex generated by the reaction of Fe 2+ with the P204 extractant is lower than that of Fe 3+ The first principle is to achieve the purpose of eluting Fe 3+ in the poisoned extractant by adding a reducing agent. The process principle adopted is essentially reduction and stripping; The agent is sodium borohydride, phosphorous acid, hydroxylamine hydrochloride or oxalic acid, and the reduction and stripping time is 0.5 to 2 hours; due to the limitation of the reduction and stripping method itself, a higher stripping temperature must be used, which will inevitably cause volatilization loss of the organic phase , also did not provide the treatment method of iron-containing waste acid.
申请号为201410155947.X专利申请公开了一种反萃负载铁的P204有机相及反萃液除铁的方法,该方法采用草酸溶液络合反萃负载Fe(III)的P204有机相,富铁反萃液采用光分解选择性沉淀除铁,当采用日光照射进行沉淀除铁时,日光照射需要的时间为4~12h,反应时间太长不利于生产上推广使用;当加入铁粉进行还原沉淀除铁时,铁粉的加入量按质量比为富铁反萃液中铁的质量的2~4倍,铁粉的加入量太大,成本太高;还原沉淀除铁时的温度需控制在60~90℃,沉淀除铁时间为4~12h,除铁后液还要进行冷却后才能返回系统使用,能耗太高,反应时间太长,对设备的耐高温耐腐蚀性的要求也高,难于在生产上推广使用;也未给出草酸亚铁的处理方法。The patent application with the application number 201410155947.X discloses a method for back-extracting the P204 organic phase loaded with iron and removing iron from the back-extraction solution. The stripping solution adopts photodecomposition to selectively precipitate and remove iron. When sunlight is used for precipitation to remove iron, the time required for sunlight is 4 to 12 hours. Too long reaction time is not conducive to popularization and use in production; when iron powder is added for reduction and precipitation When removing iron, the amount of iron powder added is 2 to 4 times the mass of iron in the iron-rich stripping solution by mass ratio. If the amount of iron powder added is too large, the cost is too high; the temperature during reduction precipitation and iron removal needs to be controlled at 60 ~90°C, the time for iron removal by precipitation is 4~12h, and the liquid after iron removal must be cooled before returning to the system for use. The energy consumption is too high, the reaction time is too long, and the requirements for high temperature resistance and corrosion resistance of the equipment are also high. It is difficult to popularize and use in production; the treatment method of ferrous oxalate has not been given.
发明内容Contents of the invention
针对现有负载铁的P204有机相在反萃技术上存在的上述问题,本发明提供一种氢氟酸反萃负载Fe3+的P204有机相及反萃液除铁循环利用的方法,该方法能够在降低反萃成本的同时,达到无废渣、废液排放的效果,绿色环保,零排放。For the P204 organic phase of existing loaded iron, the above-mentioned problems that exist in the stripping technology, the present invention provides a kind of hydrofluoric acid stripping loaded Fe3 + P204organic phase and the method for iron removal recycling of stripping solution, the method It can achieve the effect of no waste residue and waste liquid discharge while reducing the cost of stripping, which is green and environmentally friendly, and has zero discharge.
本发明的氢氟酸反萃负载Fe3+的P204有机相及反萃液除铁循环利用的方法,采用氢氟酸溶液络合反萃负载Fe3+的P204有机相,富铁反萃液采用石灰浆中和沉淀除铁、除F-,所得到的贫铁反萃液直接返回系统洗涤反萃除铁后P204有机相,或者经补充氢氟酸后继续返回反萃工序使用,沉淀渣的成分为氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用,具体步骤包括:The method for the hydrofluoric acid stripping loaded Fe3 + P204 organic phase and stripping solution for iron removal recycling of the present invention adopts hydrofluoric acid solution complexation stripping Fe3 + loaded P204 organic phase, iron-rich stripping solution Use lime slurry to neutralize and precipitate to remove iron and F - , and the obtained iron-poor stripping solution is directly returned to the system to wash the P204 organic phase after stripping and iron removal, or continue to return to the stripping process for use after supplementing hydrofluoric acid, and the precipitated residue The components are ferric hydroxide and calcium fluoride, which are recycled as slagging agents in the ferronickel pyrometallurgy process. The specific steps include:
(1)采用氢氟酸溶液作为反萃剂,将负载铁的P204有机相与反萃剂混合进行逆流反萃,获得富铁反萃液和夹带F-的空白P204有机相;该步骤当中负载铁的P204有机相中铁的反萃率为99.0%~99.5%。(1) Using hydrofluoric acid solution as the stripping agent, the P204 organic phase loaded with iron is mixed with the stripping agent for countercurrent stripping to obtain the iron - rich stripping solution and the blank P204 organic phase that entrains F-; The stripping rate of iron in the P204 organic phase of iron is 99.0%-99.5%.
(2)采用去离子水作为洗液与夹带F-的空白P204有机相进行逆流洗涤,洗涤完成后获得不含F-的空白P204有机相,该不含F-的空白P204有机相返回萃取系统循环使用;富铁反萃液中铁和F-的沉淀去除率为99.2%~99.8%。(2) Use deionized water as the washing liquid to carry out countercurrent washing with the blank P204 organic phase entrained with F- , and obtain a blank P204 organic phase without F- after washing, and return the blank P204 organic phase without F- to the extraction system Recycling; the precipitation removal rate of iron and F - in the iron-rich stripping solution is 99.2% to 99.8%.
(3)向富铁反萃液中加入石灰浆液中和沉淀除铁,反应2~4h,终点pH值控制在3.5~5.5,过滤后获得的液相为贫铁溶液,液相补充氢氟酸后返回步骤(1)中作为氢氟酸溶液循环使用,或者返回步骤(2)中作为洗液循环使用;固相为含有氢氧化铁和氟化钙的除铁渣。(3) Add lime slurry to the iron-rich stripping solution to neutralize precipitation and remove iron, react for 2-4 hours, and control the pH value at the end point at 3.5-5.5. The liquid phase obtained after filtration is an iron-poor solution, and the liquid phase is supplemented with hydrofluoric acid Return to the step (1) for recycling as a hydrofluoric acid solution, or return to the step (2) for recycling as a washing solution; the solid phase is iron removal slag containing ferric hydroxide and calcium fluoride.
所述步骤(1)中氢氟酸溶液的浓度为2~6mol/L。该氢氟酸溶液采用HF·H2O重量含量≥40%的工业氢氟酸配制。The concentration of the hydrofluoric acid solution in the step (1) is 2-6 mol/L. The hydrofluoric acid solution is prepared by using industrial hydrofluoric acid with a weight content of HF·H2O ≥ 40%.
所述步骤(1)中负载铁的P204有机相中Fe3+的含量在0.255~2.0g/L。The content of Fe3+ in the P204 organic phase loaded with iron in the step (1) is 0.255˜2.0 g/L.
所述步骤(1)中负载铁的P204有机相与反萃剂的体积比为2~6:1。In the step (1), the volume ratio of the iron-loaded P204 organic phase to the stripping agent is 2-6:1.
所述步骤(1)中逆流反萃的反萃级数为1~4级,反萃温度为25~40℃。In the step (1), the number of back-extraction stages of counter-current back-extraction is 1-4, and the back-extraction temperature is 25-40°C.
所述步骤(2)不含F-的空白P204有机相和去离子水的体积比为2~6:1。In the step (2), the volume ratio of the F - free blank P204 organic phase to the deionized water is 2-6:1.
所述步骤(2)逆流洗涤的级数为1~3级,洗涤温度为25~35℃。The number of stages of countercurrent washing in the step (2) is 1-3, and the washing temperature is 25-35°C.
所述步骤(3)中石灰浆液的浓度为10%~20%,是由CaO含量为80%的工业石灰配置而成。The lime slurry in the step (3) has a concentration of 10% to 20%, and is prepared from industrial lime with a CaO content of 80%.
所述步骤(3)中得到的除铁渣作为镍铁火法冶炼过程中的造渣剂进行回收利用。The iron removal slag obtained in the step (3) is recycled as a slagging agent in the ferronickel pyrometallurgy process.
本发明采用氢氟酸反萃负载Fe3+的P204有机相,该方法操作环境无酸雾污染,富铁反萃液采用石灰浆中和沉淀除铁、除F-,所得到的贫铁反萃液直接返回系统洗涤反萃除铁后P204有机相,或者经补充氢氟酸后继续返回反萃工序使用,沉淀渣的成分为氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用;中和沉淀剂成本低廉,也容易采购运输,解决了传统采用盐酸反萃取Fe3+的方法中存在的因盐酸为易制毒品,采购难审批,难监管,成本高,富铁的盐酸反萃液难处理的问题;本发明的方法更具有实用性,工艺简单,容易操作控制,在降低反萃成本的同时达到无废渣、废液排放的效果,绿色环保,零排放,具有高效、环保、实用性强的优点。The present invention uses hydrofluoric acid to back-extract the Fe3 + -loaded P204 organic phase. The operating environment of the method is free from acid mist pollution. The extract is directly returned to the system for washing and stripping the P204 organic phase after stripping and iron removal, or continues to return to the stripping process for use after supplementing hydrofluoric acid. The components of the precipitated slag are ferric hydroxide and calcium fluoride, which are used as The slag-forming agent is recycled; the cost of the neutralizing precipitant is low, and it is easy to purchase and transport, which solves the problems in the traditional method of extracting Fe 3+ with hydrochloric acid. Because hydrochloric acid is a precursor drug, it is difficult to approve and supervise the purchase, and the cost High, difficult to deal with iron-rich hydrochloric acid stripping solution; the method of the present invention is more practical, simple in process, easy to operate and control, and achieves the effect of no waste residue and waste liquid discharge while reducing the cost of stripping, and is green and environmentally friendly. Zero emission, with the advantages of high efficiency, environmental protection and strong practicability.
附图说明Description of drawings
图1是本发明工艺流程示意图;Fig. 1 is a schematic diagram of a process flow of the present invention;
具体实施方式Detailed ways
下面结合附图和具体实施方式,对本发明作进一步说明。The present invention will be further described below in combination with the accompanying drawings and specific embodiments.
本发明实施例中的负载Fe3+的P204有机相中萃取剂P204占总体积的10~30%,稀释剂航空煤油占总体积的70~90%。In the P204 organic phase loaded with Fe3 + in the embodiment of the present invention, the extractant P204 accounts for 10-30% of the total volume, and the diluent aviation kerosene accounts for 70-90% of the total volume.
本发明实施例中采用由市场上采购P204萃取剂和市市场上采购稀释剂航空煤油混合制成P204有机相,将P204有机相与硫酸铁的水溶液进行混合和分相,得到负载Fe3+的P204有机相。In the embodiment of the present invention, the P204 extractant and the purchased diluent aviation kerosene mixed in the market are used to make the P204 organic phase, and the P204 organic phase is mixed and phase-separated with the aqueous solution of ferric sulfate to obtain the loaded Fe3 + P204 organic phase.
本发明实施例中采用的氢氟酸为市购工业草酸;采用HF·H2O重量含量≥40%的工业氢氟酸配制氢氟酸溶液。The hydrofluoric acid used in the embodiment of the present invention is commercially available industrial oxalic acid; the hydrofluoric acid solution is prepared by using industrial hydrofluoric acid with a weight content of HF·H 2 O ≥ 40%.
本发明实施例中采用的石灰为CaO含量为80%的市购工业石灰产品。The lime used in the embodiment of the present invention is a commercially available industrial lime product with a CaO content of 80%.
本发明实施例中进行每级反萃时的混合时间为5~10min,澄清时间为5min。In the embodiment of the present invention, the mixing time for each stage of stripping is 5-10 minutes, and the clarification time is 5 minutes.
对比例:Comparative example:
盐酸除铁法:量取500ml上述负载Fe3+的P204萃取剂,配制6mol/L的盐酸溶液,然后按照相比O/A为1:1加入到载Fe3+的P204萃取剂中,进行混合反萃取10min后,取下层水相溶液,用原子吸收法测量水相中Fe3+的含量,得出Fe3+的洗脱效率为97.0%~97.6%。Hydrochloric acid iron removal method: Measure 500ml of the above-mentioned P204 extractant loaded with Fe 3+ , prepare a 6mol/L hydrochloric acid solution, and then add it to the P204 extractant loaded with Fe 3+ according to the O/A ratio of 1:1. After mixing and stripping for 10 min, the lower aqueous phase solution was taken, and the content of Fe 3+ in the aqueous phase was measured by atomic absorption method, and the elution efficiency of Fe 3+ was obtained to be 97.0%-97.6%.
实施例1:Example 1:
负载铁的P204有机相中萃取剂P204的体积占10%,Fe3+的含量在0.225g/L;用HF酸摩尔浓度为2mol/L的氢氟酸溶液作为反萃剂,将负载铁的P204有机相与反萃剂按体积比O/A为2:1混合进行逆1级反萃,反萃取时间为5min,反萃温度为25℃,反萃完成后获得富铁反萃液和空白P204有机相,负载铁的P204有机相中铁的反萃率为99.0%;将富铁反萃液采用采用加入石灰浆液中和沉淀除铁和F-,反应时间为2h;当加入石灰浆液进行还原沉淀除铁和F-时,终点pH值控制在4;将沉淀除铁后的物料过滤进行液固分离;富铁反萃液中铁和F-的沉淀去除率分别为99.2%,99.6%。分离获得的液相为贫铁溶液,补氢氟酸后作为反萃剂循环循环使用,或者直接返回洗涤P204反萃取铁后的有机相循环使用;分离得到固相除铁渣含氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用。The volume of extractant P204 accounts for 10% in the P204 organic phase of loading iron, and the content of Fe is at 0.225g/L; The hydrofluoric acid solution that is 2mol/L is used as stripping agent with HF acid molar concentration, will load iron The P204 organic phase and the stripping agent are mixed at a volume ratio of O/A of 2:1 to carry out the first-stage stripping. The stripping time is 5 minutes, and the stripping temperature is 25°C. After the stripping is completed, an iron-rich stripping solution and a blank are obtained. P204 organic phase, the stripping rate of iron in the P204 organic phase loaded with iron is 99.0%; the iron-rich stripping liquid is removed by adding lime slurry to neutralize and precipitate iron and F - , and the reaction time is 2h; when adding lime slurry to reduce When removing iron and F - by precipitation, the pH value of the end point is controlled at 4; the material after iron removal by precipitation is filtered for liquid-solid separation; the precipitation removal rates of iron and F - in the iron-rich stripping solution are 99.2% and 99.6%, respectively. The liquid phase obtained by separation is an iron-poor solution, which can be recycled as a stripping agent after hydrofluoric acid supplementation, or directly returned to the organic phase after washing P204 stripping iron for recycling; the solid phase iron removal slag containing ferric hydroxide and Calcium fluoride is recycled as a slagging agent in the ferronickel pyrometallurgy process.
实施例2:Example 2:
负载铁的P204有机相中萃取剂P204的体积占20%,Fe3+的含量在0.83g/L;用HF酸摩尔浓度为3mol/L的氢氟酸溶液作为反萃剂,将负载铁的P204有机相与反萃剂按体积比O/A为3:1混合进行逆2级反萃,反萃取时间为5min,反萃温度为30℃,反萃完成后获得富铁反萃液和空白P204有机相,负载铁的P204有机相中铁的反萃率为99.3%;将富铁反萃液采用采用加入石灰浆液中和沉淀除铁和F-,反应时间为3h;当加入石灰浆液进行还原沉淀除铁和F-时,终点pH值控制在4.5;将沉淀除铁后的物料过滤进行液固分离;富铁反萃液中铁和F-的沉淀去除率分别为99.4%,99.8%。分离获得的液相为贫铁溶液,补氢氟酸后作为反萃剂循环循环使用,或者直接返回洗涤P204反萃取铁后的有机相循环使用。分离得到固相除铁渣含氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用;The volume of extractant P204 accounts for 20% in the P204 organic phase of loading iron, and the content of Fe is at 0.83g/L; The hydrofluoric acid solution that is 3mol/L with HF acid molar concentration is as stripping agent, will load iron The P204 organic phase and the stripping agent are mixed at a volume ratio of O/A of 3:1 to carry out reverse two-stage stripping. The stripping time is 5 minutes, and the stripping temperature is 30°C. After the stripping is completed, the iron-rich stripping solution and blank are obtained. P204 organic phase, the stripping rate of iron in the P204 organic phase loaded with iron is 99.3%; the iron-rich stripping liquid is removed by adding lime slurry to neutralize and precipitate iron and F - , and the reaction time is 3h; when adding lime slurry to reduce When removing iron and F - by precipitation, the final pH value is controlled at 4.5; the material after iron removal by precipitation is filtered for liquid-solid separation; the precipitation removal rates of iron and F - in the iron-rich stripping solution are 99.4% and 99.8%, respectively. The separated liquid phase is an iron-poor solution, which can be recycled as a stripping agent after hydrofluoric acid supplementation, or directly returned to the organic phase after washing P204 and stripping iron for recycling. The solid-phase iron removal slag containing ferric hydroxide and calcium fluoride is separated and recycled as a slagging agent in the ferronickel pyrometallurgy process;
实施例3:Example 3:
负载铁的P204有机相中萃取剂P204的体积占25%,Fe3+的含量在1.35g/L;用HF酸摩尔浓度为4mol/L的氢氟酸溶液作为反萃剂,将负载铁的P204有机相与反萃剂按体积比O/A为4:1混合进行逆3级反萃,反萃取时间为8min,反萃温度为35℃,反萃完成后获得富铁反萃液和空白P204有机相,负载铁的P204有机相中铁的反萃率为99.4%;将富铁反萃液采用采用加入石灰浆液中和沉淀除铁和F-,反应时间为3h;当加入石灰浆液进行还原沉淀除铁和F-时,终点pH值控制在5;将沉淀除铁后的物料过滤进行液固分离;富铁反萃液中铁和F-的沉淀去除率分别为99.5%,99.8%。分离获得的液相为贫铁溶液,补氢氟酸后作为反萃剂循环循环使用,或者直接返回洗涤P204反萃取铁后的有机相循环使用;分离得到固相除铁渣含氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用。The volume of extractant P204 accounts for 25% in the P204 organic phase of loading iron, and the content of Fe is at 1.35g/L; The hydrofluoric acid solution that is 4mol/L with HF acid molar concentration is used as stripping agent, will load iron The P204 organic phase and the stripping agent are mixed at a volume ratio of O/A of 4:1 for reverse 3-stage stripping. The stripping time is 8 minutes, and the stripping temperature is 35°C. After the stripping is completed, iron-rich stripping solution and blank are obtained. P204 organic phase, the stripping rate of iron in the P204 organic phase loaded with iron is 99.4%; the iron-rich stripping liquid is removed by adding lime slurry to neutralize and precipitate iron and F - , and the reaction time is 3h; when adding lime slurry to reduce When removing iron and F - by precipitation, the pH value of the end point is controlled at 5; the material after iron removal by precipitation is filtered for liquid-solid separation; the precipitation removal rates of iron and F - in the iron-rich stripping solution are 99.5% and 99.8%, respectively. The liquid phase obtained by separation is an iron-poor solution, which can be recycled as a stripping agent after hydrofluoric acid supplementation, or directly returned to the organic phase after washing P204 stripping iron for recycling; the solid phase iron removal slag containing ferric hydroxide and Calcium fluoride is recycled as a slagging agent in the ferronickel pyrometallurgy process.
实施例4:Example 4:
负载铁的P204有机相中萃取剂P204的体积占30%,Fe3+的含量在1.96g/L;用HF酸摩尔浓度为6mol/L的氢氟酸溶液作为反萃剂,将负载铁的P204有机相与反萃剂按体积比O/A为5:1混合进行逆4级反萃,反萃取时间为10min,反萃温度为40℃,反萃完成后获得富铁反萃液和空白P204有机相,负载铁的P204有机相中铁的反萃率为99.5%;将富铁反萃液采用采用加入石灰浆液中和沉淀除铁和F-,反应时间为4h;当加入石灰浆液进行还原沉淀除铁和F-时,终点pH值控制在5.5;将沉淀除铁后的物料过滤进行液固分离;富铁反萃液中铁和F-的沉淀去除率分别为99.2%,99.7%。分离获得的液相为贫铁溶液,补氢氟酸后作为反萃剂循环循环使用,或者直接返回洗涤P204反萃取铁后的有机相循环使用;分离得到固相除铁渣含氢氧化铁和氟化钙,作为镍铁火法冶炼过程中的造渣剂进行回收利用。The volume of extractant P204 accounts for 30% in the P204 organic phase of loading iron, and the content of Fe is at 1.96g/L; The hydrofluoric acid solution that is 6mol/L with HF acid molar concentration is as stripping agent, will load iron The P204 organic phase and the stripping agent are mixed at a volume ratio of O/A of 5:1 for reverse 4-stage stripping. The stripping time is 10 minutes, and the stripping temperature is 40°C. After the stripping is completed, iron-rich stripping solution and blank are obtained. P204 organic phase, the stripping rate of iron in the P204 organic phase loaded with iron is 99.5%; the iron-rich stripping liquid is removed by adding lime slurry to neutralize and precipitate iron and F - , and the reaction time is 4h; when adding lime slurry to reduce When removing iron and F- by precipitation , the final pH value is controlled at 5.5; the material after iron removal by precipitation is filtered for liquid-solid separation; the precipitation removal rates of iron and F- in the iron-rich stripping solution are 99.2% and 99.7%, respectively. The liquid phase obtained by separation is an iron-poor solution, which can be recycled as a stripping agent after hydrofluoric acid supplementation, or directly returned to the organic phase after washing P204 stripping iron for recycling; the solid phase iron removal slag containing ferric hydroxide and Calcium fluoride is recycled as a slagging agent in the ferronickel pyrometallurgy process.
Claims (9)
- A kind of 1. Fe loaded in hydrofluoric acid back extraction P204 organic phases3+And the method for strip liquor processing, it is characterised in that specific step Suddenly include:(1) the P204 organic phases of load iron are mixed with back washing agent and carry out countercurrent reextraction as back washing agent using hydrofluoric acid solution Take, obtain rich iron strip liquor and entrainment F-Blank P204 organic phases;(2) using deionized water as washing lotion and entrainment F-Blank P204 organic phases carry out countercurrent washing, obtained after the completion of washing Without F-Blank P204 organic phases, should F be free of-Blank P204 organic phases return extracting system recycle;(3) lime slurry neutralization precipitation iron removaling is added into rich iron strip liquor, reacts 2~4h, endpoint pH control 3.5~ 5.5, the liquid phase obtained after filtering is poor ferrous solution, and the middle conduct hydrofluoric acid solution of return to step (1) follows after liquid phase supplements hydrofluoric acid Ring uses, or is recycled in return to step (2) as washing lotion;Solid phase is the iron dross removing containing iron hydroxide and calcirm-fluoride.
- 2. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:The concentration of hydrofluoric acid solution is 2~6mol/L in the step (1).
- 3. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:Fe in the P204 organic phases of load iron in the step (1)3+Content in 0.255~2.0g/L.
- 4. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:The P204 organic phases of load iron and the volume ratio of back washing agent are 2~6 in the step (1):1.
- 5. the Fe loaded in the hydrofluoric acid back extraction P204 organic phases according to claim 1 or 43+And the side of strip liquor processing Method, it is characterised in that:The back extraction series of countercurrent reextraction is 1~4 grade in the step (1), and back extraction temperature is 25~40 DEG C.
- 6. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:The step (2) is free of F-Blank P204 organic phases and deionized water volume ratio be 2~6:1.
- 7. the Fe loaded in the hydrofluoric acid back extraction P204 organic phases according to claim 1 or 63+And the side of strip liquor processing Method, it is characterised in that:The series of step (2) countercurrent washing is 1~3 grade, and wash temperature is 25~35 DEG C.
- 8. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:The concentration of lime slurry is 10%~20% in the step (3).
- 9. the Fe loaded in hydrofluoric acid back extraction P204 organic phases according to claim 13+And the method for strip liquor processing, its It is characterised by:The iron dross removing obtained in the step (3) is recycled as the slag former during ferronickel pyrometallurgical smelting.
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