CN106636651B - The separation method of chromium and iron aluminium in a kind of sulfuric acid system solution of aluminium containing ferrochrome - Google Patents
The separation method of chromium and iron aluminium in a kind of sulfuric acid system solution of aluminium containing ferrochrome Download PDFInfo
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- CN106636651B CN106636651B CN201611167725.5A CN201611167725A CN106636651B CN 106636651 B CN106636651 B CN 106636651B CN 201611167725 A CN201611167725 A CN 201611167725A CN 106636651 B CN106636651 B CN 106636651B
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- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 title claims abstract description 132
- 239000011651 chromium Substances 0.000 title claims abstract description 103
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 title claims abstract description 74
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 title claims abstract description 67
- 229910052804 chromium Inorganic materials 0.000 title claims abstract description 61
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 title claims abstract description 50
- 229910052742 iron Inorganic materials 0.000 title claims abstract description 48
- 229910052782 aluminium Inorganic materials 0.000 title claims abstract description 47
- 238000000926 separation method Methods 0.000 title claims abstract description 46
- 229910000604 Ferrochrome Inorganic materials 0.000 title claims description 5
- 239000004411 aluminium Substances 0.000 title claims 9
- 238000001556 precipitation Methods 0.000 claims abstract description 27
- 239000002131 composite material Substances 0.000 claims abstract description 26
- 239000000706 filtrate Substances 0.000 claims abstract description 20
- 229910019142 PO4 Inorganic materials 0.000 claims abstract description 19
- 239000010452 phosphate Substances 0.000 claims abstract description 18
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims abstract description 16
- GRWVQDDAKZFPFI-UHFFFAOYSA-H chromium(III) sulfate Chemical compound [Cr+3].[Cr+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O GRWVQDDAKZFPFI-UHFFFAOYSA-H 0.000 claims abstract description 14
- WBJZTOZJJYAKHQ-UHFFFAOYSA-K iron(3+) phosphate Chemical compound [Fe+3].[O-]P([O-])([O-])=O WBJZTOZJJYAKHQ-UHFFFAOYSA-K 0.000 claims abstract description 13
- ILRRQNADMUWWFW-UHFFFAOYSA-K aluminium phosphate Chemical compound O1[Al]2OP1(=O)O2 ILRRQNADMUWWFW-UHFFFAOYSA-K 0.000 claims abstract description 11
- 239000007800 oxidant agent Substances 0.000 claims abstract description 6
- 239000000243 solution Substances 0.000 claims description 52
- HEMHJVSKTPXQMS-UHFFFAOYSA-M sodium hydroxide Inorganic materials [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 30
- 238000003756 stirring Methods 0.000 claims description 21
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 claims description 16
- LWIHDJKSTIGBAC-UHFFFAOYSA-K tripotassium phosphate Chemical compound [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 claims description 14
- 239000007788 liquid Substances 0.000 claims description 10
- 239000010802 sludge Substances 0.000 claims description 9
- 239000001488 sodium phosphate Substances 0.000 claims description 9
- 229910000162 sodium phosphate Inorganic materials 0.000 claims description 9
- RYFMWSXOAZQYPI-UHFFFAOYSA-K trisodium phosphate Chemical compound [Na+].[Na+].[Na+].[O-]P([O-])([O-])=O RYFMWSXOAZQYPI-UHFFFAOYSA-K 0.000 claims description 9
- -1 iron ion Chemical class 0.000 claims description 8
- 239000002699 waste material Substances 0.000 claims description 8
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 claims description 7
- 238000009713 electroplating Methods 0.000 claims description 7
- 229910000160 potassium phosphate Inorganic materials 0.000 claims description 7
- 235000011009 potassium phosphates Nutrition 0.000 claims description 7
- 239000007864 aqueous solution Substances 0.000 claims description 4
- 230000001590 oxidative effect Effects 0.000 claims description 4
- 229920006395 saturated elastomer Polymers 0.000 claims description 4
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- 239000005955 Ferric phosphate Substances 0.000 claims 3
- 229940032958 ferric phosphate Drugs 0.000 claims 3
- 229910000399 iron(III) phosphate Inorganic materials 0.000 claims 3
- REDXJYDRNCIFBQ-UHFFFAOYSA-N aluminium(3+) Chemical compound [Al+3] REDXJYDRNCIFBQ-UHFFFAOYSA-N 0.000 claims 2
- 238000000034 method Methods 0.000 abstract description 25
- KJAZZOWIUGBRCT-UHFFFAOYSA-K aluminum;iron(2+);phosphate Chemical compound [Al+3].[Fe+2].[O-]P([O-])([O-])=O KJAZZOWIUGBRCT-UHFFFAOYSA-K 0.000 abstract description 21
- 238000011084 recovery Methods 0.000 abstract description 16
- 229910000398 iron phosphate Inorganic materials 0.000 abstract description 10
- KCZFLPPCFOHPNI-UHFFFAOYSA-N alumane;iron Chemical compound [AlH3].[Fe] KCZFLPPCFOHPNI-UHFFFAOYSA-N 0.000 abstract description 5
- 230000000694 effects Effects 0.000 abstract description 4
- 230000008901 benefit Effects 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 229910052751 metal Inorganic materials 0.000 abstract description 3
- 239000002184 metal Substances 0.000 abstract description 3
- 239000000126 substance Substances 0.000 abstract description 3
- 238000009854 hydrometallurgy Methods 0.000 abstract description 2
- 239000011259 mixed solution Substances 0.000 description 10
- 235000021317 phosphate Nutrition 0.000 description 10
- 238000012360 testing method Methods 0.000 description 9
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 6
- 238000002386 leaching Methods 0.000 description 5
- 239000000047 product Substances 0.000 description 5
- 238000006479 redox reaction Methods 0.000 description 5
- 229910000151 chromium(III) phosphate Inorganic materials 0.000 description 4
- IKZBVTPSNGOVRJ-UHFFFAOYSA-K chromium(iii) phosphate Chemical compound [Cr+3].[O-]P([O-])([O-])=O IKZBVTPSNGOVRJ-UHFFFAOYSA-K 0.000 description 4
- 239000002244 precipitate Substances 0.000 description 4
- 238000000605 extraction Methods 0.000 description 3
- 229940062993 ferrous oxalate Drugs 0.000 description 3
- OWZIYWAUNZMLRT-UHFFFAOYSA-L iron(2+);oxalate Chemical compound [Fe+2].[O-]C(=O)C([O-])=O OWZIYWAUNZMLRT-UHFFFAOYSA-L 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- XYFCBTPGUUZFHI-UHFFFAOYSA-N Phosphine Chemical compound P XYFCBTPGUUZFHI-UHFFFAOYSA-N 0.000 description 2
- 235000011124 aluminium ammonium sulphate Nutrition 0.000 description 2
- LCQXXBOSCBRNNT-UHFFFAOYSA-K ammonium aluminium sulfate Chemical compound [NH4+].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O LCQXXBOSCBRNNT-UHFFFAOYSA-K 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- VQWFNAGFNGABOH-UHFFFAOYSA-K chromium(iii) hydroxide Chemical compound [OH-].[OH-].[OH-].[Cr+3] VQWFNAGFNGABOH-UHFFFAOYSA-K 0.000 description 2
- 229940116007 ferrous phosphate Drugs 0.000 description 2
- 239000011790 ferrous sulphate Substances 0.000 description 2
- 235000003891 ferrous sulphate Nutrition 0.000 description 2
- 239000002440 industrial waste Substances 0.000 description 2
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 2
- 229910000155 iron(II) phosphate Inorganic materials 0.000 description 2
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 2
- SDEKDNPYZOERBP-UHFFFAOYSA-H iron(ii) phosphate Chemical compound [Fe+2].[Fe+2].[Fe+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O SDEKDNPYZOERBP-UHFFFAOYSA-H 0.000 description 2
- 235000006408 oxalic acid Nutrition 0.000 description 2
- 229910017119 AlPO Inorganic materials 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000012670 alkaline solution Substances 0.000 description 1
- 229940037003 alum Drugs 0.000 description 1
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 229910001430 chromium ion Inorganic materials 0.000 description 1
- 229910000423 chromium oxide Inorganic materials 0.000 description 1
- DJLCOAPFZCDZQW-UHFFFAOYSA-N chromium phosphoric acid Chemical compound [Cr].OP(O)(O)=O DJLCOAPFZCDZQW-UHFFFAOYSA-N 0.000 description 1
- OSXYJBRVRDSPSW-UHFFFAOYSA-J chromium(3+) hydroxide phosphate Chemical compound [OH-].[Cr+3].P(=O)([O-])([O-])[O-].[Cr+3] OSXYJBRVRDSPSW-UHFFFAOYSA-J 0.000 description 1
- 238000000658 coextraction Methods 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- IMBKASBLAKCLEM-UHFFFAOYSA-L ferrous ammonium sulfate (anhydrous) Chemical compound [NH4+].[NH4+].[Fe+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O IMBKASBLAKCLEM-UHFFFAOYSA-L 0.000 description 1
- 229910052598 goethite Inorganic materials 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- AEIXRCIKZIZYPM-UHFFFAOYSA-M hydroxy(oxo)iron Chemical compound [O][Fe]O AEIXRCIKZIZYPM-UHFFFAOYSA-M 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 229940085991 phosphate ion Drugs 0.000 description 1
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 1
- 229910000073 phosphorus hydride Inorganic materials 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000004575 stone 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
- C22B7/00—Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
- C22B7/006—Wet processes
-
- 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
- C22B21/00—Obtaining aluminium
- C22B21/0015—Obtaining aluminium by wet processes
- C22B21/0023—Obtaining aluminium by wet processes from waste materials
-
- 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
- C22B34/00—Obtaining refractory metals
- C22B34/30—Obtaining chromium, molybdenum or tungsten
- C22B34/32—Obtaining chromium
-
- 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)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Manufacture And Refinement Of Metals (AREA)
Abstract
本发明属于湿法冶金技术领域,涉及一种含铬铁铝的硫酸体系溶液中铬和铁铝的分离方法。该方法包括如下步骤:1)加入氧化剂进行预处理;2)调节溶液至特定pH值,加入磷酸盐并在特定温度下反应,得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;3)调节滤液至特定pH值,再次加入磷酸盐并在特定温度下反应,得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液,完成铬与铁铝的分离。该方法流程短、操作简单,易于大规模应用;采用磷酸盐分步沉淀的方法,具有较强的选择性和较理想的分离效果;金属铬的回收率大于98%,经济效益显著;整个分离过程未使用可能对环境造成危害的化学物质,符合绿色环保的要求。The invention belongs to the technical field of hydrometallurgy and relates to a method for separating chromium and iron and aluminum in a sulfuric acid system solution containing chromium, iron and aluminum. The method comprises the following steps: 1) adding an oxidizing agent for pretreatment; 2) adjusting the solution to a specific pH value, adding phosphate and reacting at a specific temperature to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate; 3) Adjust the filtrate to a specific pH value, add phosphate again and react at a specific temperature to obtain iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate and chromium sulfate solution to complete the separation of chromium and iron-aluminum. The method has short flow, simple operation, and is easy to be applied on a large scale; adopting the step-by-step precipitation method of phosphate has strong selectivity and ideal separation effect; the recovery rate of metal chromium is greater than 98%, and the economic benefit is remarkable; the whole separation process No chemical substances that may cause harm to the environment are used, which meets the requirements of green environmental protection.
Description
技术领域technical field
本发明属于湿法冶金技术领域。The invention belongs to the technical field of hydrometallurgy.
背景技术Background technique
在电镀污泥资源化利用的过程中,硫酸是一种常用的湿法冶金浸出溶剂,其浸出效率高,浸出效果好,因而使用广泛。硫酸浸出使用PAC(聚合氯化铝)作为絮凝剂,形成含有硫酸铬、硫酸铝、硫酸亚铁的混合溶液。由于铬、铁、铝三种元素的原子半径相近,化学性质相似,因此存在分离困难的问题。In the process of resource utilization of electroplating sludge, sulfuric acid is a commonly used hydrometallurgical leaching solvent, which has high leaching efficiency and good leaching effect, so it is widely used. Sulfuric acid leaching uses PAC (polyaluminum chloride) as a flocculant to form a mixed solution containing chromium sulfate, aluminum sulfate, and ferrous sulfate. Since the atomic radii of chromium, iron, and aluminum are similar and their chemical properties are similar, there is a problem of difficulty in separation.
目前已开发的硫酸体系中铬和铁的分离方法主要包括以下几种:(1)溶剂萃取法:该方法具有设备简单、过程易于控制以及试剂可循环使用等特点,经膦类萃取剂(如P204、P507)萃取,虽然铁的萃取率可达99%以上,但是铬的共萃取率也高达25%,分离效果不佳,铬损失明显;(2)莫尔盐结晶法:该方法基于硫酸亚铁、硫酸铬与硫酸铵反应,生成的铬铵矾和亚铁铵矾存在明显的溶解度差异,亚铁铵矾结晶析出,而铬则停留在溶液中,达到分离铬铁的目的,并且铬的损失率较低,但是该方法工序复杂,操作要求严格,不易大规模工业化应用;(3)草酸亚铁沉淀法:该方法基于草酸亚铁溶度积低的原理,通过加入草酸来沉淀铁元素,以达到分离铬和铁的目的,但是除铁率对于草酸加入量及温度等因素极为敏感,操作要求严格,并且较佳的反应pH值约为4.0,初始溶液中和负荷大,也不易大规模推广使用;(4)针铁矿法:该方法从混合溶液中除铁并回收铬,虽然除铁率高达99%,但是铬的损失率也较高,约为15%;(5)磷酸盐沉铬法:该方法基于磷酸铬与磷酸亚铁的溶解度差异来实现铬与亚铁的分离,虽然可实现98%的铬回收率,但是反应需要加热,并且生成物为磷酸铬与氢氧化铬的复合沉淀物,后续需要再生。The separation method of chromium and iron in the sulfuric acid system that has been developed at present mainly comprises the following several: (1) solvent extraction method: this method has characteristics such as equipment is simple, process is easy to control and reagent can be recycled, through phosphine extraction agent (such as P204, P507) extraction, although the extraction rate of iron can reach more than 99%, the co-extraction rate of chromium is also up to 25%, the separation effect is not good, and the loss of chromium is obvious; (2) Mohr's salt crystallization method: this method is based on sulfuric acid Ferrous, chromium sulfate reacts with ammonium sulfate, and there is an obvious solubility difference between the chromammonium alum and ferrous ammonium alum, and the ferrous ammonium alum crystallizes out, while the chromium stays in the solution to achieve the purpose of separating ferrochrome, and the chromium The loss rate of ferrous oxalate is relatively low, but the method is complicated in operation and strict in operation requirements, and is not easy for large-scale industrial application; (3) ferrous oxalate precipitation method: this method is based on the principle of low solubility product of ferrous oxalate, and precipitates iron by adding oxalic acid Elements, in order to achieve the purpose of separating chromium and iron, but the iron removal rate is extremely sensitive to factors such as the amount of oxalic acid added and temperature, the operation requirements are strict, and the optimal reaction pH value is about 4.0, the initial solution has a large neutralization load, and it is not easy Large-scale promotion and use; (4) goethite method: this method removes iron and reclaims chromium from the mixed solution, although the iron removal rate is as high as 99%, the loss rate of chromium is also higher, about 15%; (5) Phosphate chromium precipitation method: This method realizes the separation of chromium and ferrous phosphate based on the solubility difference between chromium phosphate and ferrous phosphate. Although a chromium recovery rate of 98% can be achieved, the reaction requires heating, and the products are chromium phosphate and hydrogen Composite deposits of chromium oxide that subsequently require regeneration.
目前已开发的铬和铝的分离方法主要通过在碱性条件下,将三价铬氧化为六价铬,而铝则以偏铝酸盐的形式存在,加酸调节pH值至8.0,铝能够以氢氧化铝沉淀的形式实现与离子态铬的分离。The currently developed separation method of chromium and aluminum mainly oxidizes trivalent chromium to hexavalent chromium under alkaline conditions, while aluminum exists in the form of metaaluminate, adding acid to adjust the pH value to 8.0, aluminum can Separation from ionic chromium is achieved in the form of aluminum hydroxide precipitates.
申请号为200710041574.3的中国发明专利公开了一种电镀污泥的磷酸盐稳定化处理方法,其主要步骤如下:(1)将电镀污泥经102℃烘干,然后研磨成粉,备用;(2)在30~70℃温度范围内,将分析纯的可溶性磷酸盐与上述电镀污泥按1:70~90的重量比例混合,并在搅拌机中强力搅拌4小时,使其充分反应,反应过程中控制pH值在8~11范围内;(3)反应结束后,自然冷却,得到含有重金属复合磷酸盐的污泥固体样品,试验表明该污泥能达到国家规定的危险废物填埋标准。然而,该方法仅仅是电镀污泥的稳定化处理,没有实现有价金属的资源化利用。The Chinese invention patent with application number 200710041574.3 discloses a phosphate stabilization treatment method for electroplating sludge. The main steps are as follows: (1) drying the electroplating sludge at 102° C., and then grinding it into powder for later use; (2) ) in the temperature range of 30-70°C, mix the analytically pure soluble phosphate with the above-mentioned electroplating sludge in a weight ratio of 1:70-90, and stir vigorously in a mixer for 4 hours to make it fully react, during the reaction process Control the pH value in the range of 8 to 11; (3) After the reaction, cool naturally to obtain a solid sample of sludge containing heavy metal compound phosphate, and the test shows that the sludge can meet the national hazardous waste landfill standard. However, this method only stabilizes electroplating sludge, and does not realize the resource utilization of valuable metals.
申请号为201310008199.8的中国发明专利公开了一种硫酸体系溶液中铬和铁的选择性分离方法,其主要步骤如下:(1)在含铬和铁的硫酸体系溶液中,加入还原剂进行预处理;(2)调整溶液pH值;(3)加入可溶性磷酸盐,进行选择性磷酸沉铬反应,形成磷酸铬与氢氧化铬的复合沉淀物;(4)进行过滤分离,得到磷酸铬氢氧化铬复合沉淀物和含硫酸亚铁溶液,实现铬铁选择性分离。该方法虽然可以实现98%以上的铬回收率,然而适用的铬离子浓度较低(0.1~30g/L),导致处理规模较大,难以大规模工业化应用。The Chinese invention patent with application number 201310008199.8 discloses a selective separation method for chromium and iron in a sulfuric acid system solution, the main steps of which are as follows: (1) adding a reducing agent to the sulfuric acid system solution containing chromium and iron for pretreatment (2) adjust the pH value of the solution; (3) add soluble phosphate, carry out selective phosphoric acid chromium precipitation reaction, form the composite precipitate of chromium phosphate and chromium hydroxide; (4) carry out filtration separation, obtain chromium phosphate chromium hydroxide Composite precipitate and solution containing ferrous sulfate to achieve selective separation of ferrochromium. Although this method can achieve a chromium recovery rate of more than 98%, the applicable chromium ion concentration is low (0.1-30g/L), which leads to a large processing scale and is difficult for large-scale industrial application.
发明内容Contents of the invention
针对上述现有技术中存在的问题,本发明旨在提供一种工艺流程短、操作简单、环境友好、易于大规模应用的含铬铁铝的硫酸体系溶液中铬和铁铝的分步选择性分离方法。Aiming at the problems existing in the above-mentioned prior art, the present invention aims to provide a step-by-step selectivity of chromium and iron-aluminum in the sulfuric acid system solution containing chromium-iron-aluminum with short process flow, simple operation, environmental friendliness and easy large-scale application. Separation method.
具体而言,本发明采用如下技术方案:Specifically, the present invention adopts the following technical solutions:
一种含铬铁铝的硫酸体系溶液中铬和铁铝的分离方法,其包括如下步骤:A method for separating chromium and iron and aluminum in a sulfuric acid system solution containing chromium, iron and aluminum, comprising the steps of:
1)向含Cr3+、Fe2+、Al3+的硫酸体系溶液中加入氧化剂,直至溶液中的铬、铁、铝元素分别仅以Cr3+、Fe3+、Al3+形式存在;1) Add an oxidizing agent to the sulfuric acid system solution containing Cr 3+ , Fe 2+ , and Al 3+ until the chromium, iron, and aluminum elements in the solution only exist in the form of Cr 3+ , Fe 3+ , and Al 3+ ;
2)向步骤1)中的溶液中加入碱液,直至pH=1~3,按照磷酸根离子与溶液中的铁离子和铝离子之和的摩尔比为0.2~0.7:1的比例,加入可溶性磷酸盐,并在5~60℃条件下保温搅拌,过滤得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;2) Add lye to the solution in step 1) until pH = 1 to 3, and add soluble Phosphate, and insulated and stirred at 5-60°C, filtered to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate;
3)向步骤2)中的滤液中加入碱液,直至pH=2~4,按照磷酸根离子与滤液中的铝离子的摩尔比为0.6~1.6:1的比例,加入可溶性磷酸盐,并在5~60℃条件下保温搅拌,过滤得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液,完成含铬铁铝的硫酸体系溶液中铬与铁铝的分离。3) Add lye to the filtrate in step 2), until pH=2~4, according to the molar ratio of phosphate ion and aluminum ion in the filtrate is the ratio of 0.6~1.6:1, add soluble phosphate, and in Keep stirring at 5-60°C, filter to obtain iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate and chromium sulfate solution, and complete the separation of chromium and iron-aluminum in the sulfuric acid system solution containing chromium-iron-aluminum.
在上述分离方法中,步骤1)中所述含Cr3+、Fe2+、Al3+的硫酸体系溶液为电镀污泥硫酸浸出液。In the above separation method, the sulfuric acid system solution containing Cr 3+ , Fe 2+ , and Al 3+ in step 1) is an electroplating sludge sulfuric acid leaching solution.
在上述分离方法中,步骤1)中所述含Cr3+、Fe2+、Al3+的硫酸体系溶液中Cr3+的质量浓度为10~80g/L,Fe2+的质量浓度为0.5~4g/L,Al3+的质量浓度为0.5~4g/L。In the above separation method, the mass concentration of Cr 3+ in the sulfuric acid system solution containing Cr 3+ , Fe 2+ , and Al 3+ in step 1) is 10-80 g/L, and the mass concentration of Fe 2+ is 0.5 ~4g/L, the mass concentration of Al 3+ is 0.5~4g/L.
在上述分离方法中,步骤1)中所述氧化剂为含Cr6+的废液。利用Cr6+与Fe2+之间的氧化还原反应,不仅可以将硫酸体系溶液中的Fe2+氧化成Fe3+,同时可以将工业废液中的Cr6 +还原成Cr3+,随后连同硫酸体系溶液中的Cr3+一起进行后续选择性分离。In the above separation method, the oxidant in step 1) is waste liquid containing Cr 6+ . Utilizing the redox reaction between Cr 6+ and Fe 2+ , not only can Fe 2+ in sulfuric acid system solution be oxidized to Fe 3+ , but also Cr 6+ in industrial waste liquid can be reduced to Cr 3+ , and then Subsequent selective separation is carried out together with Cr 3+ in the sulfuric acid system solution.
在上述分离方法中,步骤2)中所述碱液为氢氧化钠或氢氧化钾的饱和水溶液。In the above separation method, the alkaline solution in step 2) is a saturated aqueous solution of sodium hydroxide or potassium hydroxide.
在上述分离方法中,步骤2)中所述可溶性磷酸盐为磷酸钠或磷酸钾。In the above separation method, the soluble phosphate in step 2) is sodium phosphate or potassium phosphate.
在上述分离方法中,步骤2)中所述搅拌的线速度为50~400m/min,时间为5~120min。In the above separation method, the linear velocity of the stirring in step 2) is 50-400 m/min, and the time is 5-120 min.
在上述分离方法中,步骤3)中所述碱液为氢氧化钠或氢氧化钾的饱和水溶液。In the above separation method, the lye described in step 3) is a saturated aqueous solution of sodium hydroxide or potassium hydroxide.
在上述分离方法中,步骤3)中所述可溶性磷酸盐为磷酸钠或磷酸钾。In the above separation method, the soluble phosphate in step 3) is sodium phosphate or potassium phosphate.
在上述分离方法中,步骤3)中所述搅拌的线速度为50~400m/min,时间为5~120min。In the above separation method, the linear velocity of the stirring in step 3) is 50-400 m/min, and the time is 5-120 min.
本发明的分离方法利用了Cr3+、Fe3+、Al3+各自对应的磷酸盐的溶解度差异,实现了硫酸体系溶液中铬与铁铝的选择性分离。由于CrPO4·2H2O的溶度积(Ksp)为2.4×10-23,FePO4·2H2O的溶度积为9.9×10-16,AlPO4的溶度积为6.3×10-19,因此通过调整pH值和温度、进行化学沉淀反应、过滤分离等工艺步骤可以得到磷酸铁铝复合沉淀和硫酸铬溶液,实现铬和铁铝的最终分离。The separation method of the present invention utilizes the solubility differences of phosphates corresponding to Cr 3+ , Fe 3+ , and Al 3+ respectively, and realizes the selective separation of chromium and iron and aluminum in the sulfuric acid system solution. Since the solubility product (Ksp) of CrPO 4 ·2H 2 O is 2.4×10 -23 , the solubility product of FePO 4 ·2H 2 O is 9.9×10-16, and the solubility product of AlPO 4 is 6.3×10-19 Therefore, by adjusting the pH value and temperature, carrying out chemical precipitation reaction, filtration and separation and other process steps, the iron-aluminum phosphate composite precipitation and chromium sulfate solution can be obtained, and the final separation of chromium and iron-aluminum can be realized.
由现有技术相比,采用上述技术方案的本发明具有以下优点:Compared with the prior art, the present invention adopting the technical solution has the following advantages:
(1)工艺流程短、操作简单、成本低,易于实现大规模工业化应用;(1) The process flow is short, the operation is simple, the cost is low, and it is easy to realize large-scale industrial application;
(2)采用磷酸盐分步沉淀铁和铝,可以在较宽的离子浓度范围内具有较强的选择性和较理想的分离效果;(2) Using phosphate to precipitate iron and aluminum step by step can have strong selectivity and ideal separation effect in a wide range of ion concentration;
(3)硫酸体系溶液中的金属铬得到有效回收,回收率大于98%,经济效益显著;(3) Metal chromium in the sulfuric acid system solution is effectively recovered, the recovery rate is greater than 98%, and the economic benefit is remarkable;
(4)硫酸体系溶液的预处理过程中可以使用含六价铬的工业废液作为氧化剂,既可实现高价铬废液的二次利用,又可将高价铬废液中的铬元素一并回收,一举两得;(4) In the pretreatment process of sulfuric acid system solution, industrial waste liquid containing hexavalent chromium can be used as oxidant, which can not only realize the secondary utilization of high-valent chromium waste liquid, but also recover the chromium element in high-valent chromium waste liquid , kill two birds with one stone;
(5)整个分离过程未使用可能对环境造成危害的化学物质,符合绿色环保的要求。(5) The entire separation process does not use chemical substances that may cause harm to the environment, which meets the requirements of green environmental protection.
具体实施方式Detailed ways
下文将结合具体的实施例对本发明的技术方案做出进一步的阐述。除非另有说明,下列实施例中所使用的仪器、材料和试剂等均可通过常规商业手段获得。The technical solutions of the present invention will be further described below in conjunction with specific embodiments. Unless otherwise stated, the instruments, materials and reagents used in the following examples can be obtained through conventional commercial means.
实施例1:含铬铁铝的硫酸体系溶液中铬和铁铝的分离。Example 1: Separation of chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum.
(1)向含铬铁铝的硫酸体系溶液(其中Cr3+的质量浓度为49.3g/L,Fe2+的质量浓度为2.1g/L,Al3+的质量浓度为2.13g/L)中加入含Cr6+的废液,通过氧化还原反应将Fe2+氧化成Fe3+,同时将Cr6+还原成Cr3+,直至混合溶液中的铬、铁、铝元素分别仅以Cr3+、Fe3+、Al3+形式存在;(1) to the sulfuric acid system solution containing chromium, iron and aluminum (wherein the mass concentration of Cr 3+ is 49.3g/L, the mass concentration of Fe 2+ is 2.1g/L, and the mass concentration of Al 3+ is 2.13g/L) Add waste liquid containing Cr 6+ into the solution, oxidize Fe 2+ to Fe 3+ through oxidation-reduction reaction, and reduce Cr 6+ to Cr 3+ at the same time, until the chromium, iron, and aluminum elements in the mixed solution are only composed of Cr Exist in the form of 3+ , Fe 3+ , Al 3+ ;
(2)向步骤(1)中的混合溶液中加入饱和氢氧化钠溶液,直至pH=2.0,按照n(PO4 3-):n(Fe3++Al3+)=0.5:1的摩尔比,加入磷酸钠,并在5℃条件下保温搅拌10min,搅拌线速度控制在150m/min,过滤得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为48.8g/L、0.2g/L、1.4g/L;(2) Add saturated sodium hydroxide solution to the mixed solution in step (1) until pH=2.0, according to the mole of n(PO 4 3- ):n(Fe 3+ +Al 3+ )=0.5:1 Add sodium phosphate, keep stirring at 5°C for 10 minutes, control the stirring line speed at 150m/min, filter to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate; after testing, Cr 3+ , The mass concentrations of Fe 3+ and Al 3+ are 48.8g/L, 0.2g/L and 1.4g/L respectively;
(3)向步骤(2)中的滤液中加入饱和氢氧化钠溶液,直至pH=3.0,按照n(PO4 3-):n(Al3+)=1.2:1的摩尔比,加入磷酸钠,并在5℃条件下保温搅拌10min,搅拌线速度控制在150m/min,过滤得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为48.4g/L、0.003g/L、0.141g/L。(3) Add saturated sodium hydroxide solution to the filtrate in step (2) until pH=3.0, according to the molar ratio of n(PO 4 3- ):n(Al 3+ )=1.2:1, add sodium phosphate , and kept stirring at 5°C for 10 minutes, the stirring line speed was controlled at 150m/min, and filtered to obtain iron-aluminum phosphate composite precipitation and chromium sulfate solution mainly composed of aluminum phosphate; after testing, Cr 3+ and Fe 3+ in the filtrate , Al 3+ mass concentrations are 48.4g/L, 0.003g/L, 0.141g/L respectively.
经过上述3步操作,含铬铁铝的硫酸体系溶液中的铬和铁铝实现了有效分离,其中铬元素主要以硫酸铬形式溶解在溶液中,铬回收率为98.16%;铁元素主要通过以磷酸铁为主的磷酸铁铝复合沉淀得以回收,铁回收率为99.85%;铝元素主要通过以磷酸铝为主的磷酸铁铝复合沉淀得以回收,铝回收率为93.38%。After the above three steps of operation, the chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum have been effectively separated, and the chromium element is mainly dissolved in the solution in the form of chromium sulfate, and the chromium recovery rate is 98.16%; The iron-aluminum phosphate composite precipitation mainly composed of iron phosphate can be recovered, and the iron recovery rate is 99.85%; the aluminum element is mainly recovered through the iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate, and the aluminum recovery rate is 93.38%.
实施例2:含铬铁铝的硫酸体系溶液中铬和铁铝的分离。Example 2: Separation of chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum.
(1)向含铬铁铝的硫酸体系溶液(其中Cr3+的质量浓度为30g/L,Fe2+的质量浓度为1.29g/L,Al3+的质量浓度为1.25g/L)中加入含Cr6+的废液,通过氧化还原反应将Fe2+氧化成Fe3+,同时将Cr6+还原成Cr3+,直至混合溶液中的铬、铁、铝元素分别仅以Cr3+、Fe3+、Al3+形式存在;(1) In the sulfuric acid system solution containing chromium, iron and aluminum (wherein the mass concentration of Cr 3+ is 30g/L, the mass concentration of Fe 2+ is 1.29g/L, and the mass concentration of Al 3+ is 1.25g/L) Add waste liquid containing Cr 6+ , oxidize Fe 2+ to Fe 3+ through oxidation-reduction reaction, and reduce Cr 6+ to Cr 3+ at the same time, until the chromium, iron and aluminum elements in the mixed solution are only composed of Cr 3+ + , Fe 3+ , Al 3+ forms;
(2)向步骤(1)中的混合溶液中加入饱和氢氧化钠溶液,直至pH=2.1,按照n(PO4 3-):n(Fe3++Al3+)=0.53:1的摩尔比,加入磷酸钠,并在10℃条件下保温搅拌8min,搅拌线速度控制在200m/min,过滤得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为29.6g/L、0.11g/L、0.63g/L;(2) Add saturated sodium hydroxide solution to the mixed solution in step (1) until pH=2.1, according to the mole of n(PO 4 3- ):n(Fe 3+ +Al 3+ )=0.53:1 Add sodium phosphate, keep stirring at 10°C for 8 minutes, control the stirring line speed at 200m/min, filter to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate; after testing, Cr 3+ , The mass concentrations of Fe 3+ and Al 3+ are 29.6g/L, 0.11g/L and 0.63g/L respectively;
(3)向步骤(2)中的滤液中加入饱和氢氧化钠溶液,直至pH=3.3,按照n(PO4 3-):n(Al3+)=1:1的摩尔比,加入磷酸钠,并在10℃条件下保温搅拌8min,搅拌线速度控制在200m/min,过滤得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为29.4g/L、0.002g/L、0.065g/L。(3) Add saturated sodium hydroxide solution to the filtrate in step (2) until pH=3.3, according to the molar ratio of n(PO 4 3- ):n(Al 3+ )=1:1, add sodium phosphate , and kept stirring at 10°C for 8 minutes, the stirring line speed was controlled at 200m/min, and filtered to obtain iron-aluminum phosphate composite precipitation and chromium sulfate solution mainly composed of aluminum phosphate; after testing, Cr 3+ , Fe 3+ in the filtrate , Al 3+ mass concentrations were 29.4g/L, 0.002g/L, 0.065g/L, respectively.
经过上述3步操作,含铬铁铝的硫酸体系溶液中的铬和铁铝实现了有效分离,其中铬元素主要以硫酸铬形式溶解在溶液中,铬回收率为98.15%;铁元素主要通过以磷酸铁为主的磷酸铁铝复合沉淀得以回收,铁回收率为99.84%;铝元素主要通过以磷酸铝为主的磷酸铁铝复合沉淀得以回收,铝回收率为94.8%。After the above three steps of operation, the chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum have been effectively separated, wherein the chromium element is mainly dissolved in the solution in the form of chromium sulfate, and the chromium recovery rate is 98.15%; The iron-aluminum phosphate composite precipitation mainly composed of iron phosphate can be recovered, and the iron recovery rate is 99.84%. The aluminum element is mainly recovered through the iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate, and the aluminum recovery rate is 94.8%.
实施例3:含铬铁铝的硫酸体系溶液中铬和铁铝的分离。Example 3: Separation of chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum.
(1)向含铬铁铝的硫酸体系溶液(其中Cr3+的质量浓度为10.5g/L,Fe2+的质量浓度为0.56g/L,Al3+的质量浓度为0.51g/L)中加入含Cr6+的废液,通过氧化还原反应将Fe2+氧化成Fe3+,同时将Cr6+还原成Cr3+,直至混合溶液中的铬、铁、铝元素分别仅以Cr3+、Fe3+、Al3+形式存在;(1) To the sulfuric acid system solution containing chromium, iron and aluminum (wherein the mass concentration of Cr 3+ is 10.5g/L, the mass concentration of Fe 2+ is 0.56g/L, and the mass concentration of Al 3+ is 0.51g/L) Add waste liquid containing Cr 6+ to the mixture, oxidize Fe 2+ to Fe 3+ through oxidation-reduction reaction, and reduce Cr 6+ to Cr 3+ at the same time, until the chromium, iron, and aluminum elements in the mixed solution are only composed of Cr Exist in the form of 3+ , Fe 3+ , Al 3+ ;
(2)向步骤(1)中的混合溶液中加入饱和氢氧化钾溶液,直至pH=1.0,按照n(PO4 3-):n(Fe3++Al3+)=0.2:1的摩尔比,加入磷酸钾,并在30℃条件下保温搅拌20min,搅拌线速度控制在400m/min,过滤得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为10.25g/L、0.06g/L、0.26g/L;(2) Add saturated potassium hydroxide solution to the mixed solution in step (1) until pH=1.0, according to the mole of n(PO 4 3- ):n(Fe 3+ +Al 3+ )=0.2:1 Add potassium phosphate, keep stirring at 30°C for 20 minutes, control the stirring line speed at 400m/min, filter to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate; after testing, Cr 3+ , The mass concentrations of Fe 3+ and Al 3+ are 10.25g/L, 0.06g/L and 0.26g/L respectively;
(3)向步骤(2)中的滤液中加入饱和氢氧化钾溶液,直至pH=2.0,按照n(PO4 3-):n(Al3+)=1.2:1的摩尔比,加入磷酸钠,并在30℃条件下保温搅拌20min,搅拌线速度控制在400m/min,过滤得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为10.29g/L、0.001g/L、0.046g/L。(3) Add saturated potassium hydroxide solution to the filtrate in step (2) until pH=2.0, according to the molar ratio of n(PO 4 3- ):n(Al 3+ )=1.2:1, add sodium phosphate , and kept stirring at 30°C for 20 minutes, the stirring line speed was controlled at 400m/min, and filtered to obtain iron-aluminum phosphate composite precipitation and chromium sulfate solution mainly composed of aluminum phosphate; after testing, Cr 3+ , Fe 3+ in the filtrate , Al 3+ mass concentrations are 10.29g/L, 0.001g/L, 0.046g/L respectively.
经过上述3步操作,含铬铁铝的硫酸体系溶液中的铬和铁铝实现了有效分离,其中铬元素主要以硫酸铬形式溶解在溶液中,铬回收率为98.03%;铁元素主要通过以磷酸铁为主的磷酸铁铝复合沉淀得以回收,铁回收率为99.82%;铝元素主要通过以磷酸铝为主的磷酸铁铝复合沉淀得以回收,铝回收率为90.98%。After the above three steps of operation, the chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum have been effectively separated, and the chromium element is mainly dissolved in the solution in the form of chromium sulfate, and the chromium recovery rate is 98.03%; The iron-aluminum phosphate composite precipitation mainly composed of iron phosphate can be recovered, and the iron recovery rate is 99.82%; the aluminum element is mainly recovered through the iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate, and the aluminum recovery rate is 90.98%.
实施例4:含铬铁铝的硫酸体系溶液中铬和铁铝的分离。Example 4: Separation of chromium and iron and aluminum in the sulfuric acid system solution containing chromium, iron and aluminum.
(1)向含铬铁铝的硫酸体系溶液(其中Cr3+的质量浓度为81.3g/L,Fe2+的质量浓度为4.56g/L,Al3+的质量浓度为4.23g/L)中加入含Cr6+的废液,通过氧化还原反应将Fe2+氧化成Fe3+,同时将Cr6+还原成Cr3+,直至混合溶液中的铬、铁、铝元素分别仅以Cr3+、Fe3+、Al3+形式存在;(1) to the sulfuric acid system solution containing chromium, iron and aluminum (wherein the mass concentration of Cr 3+ is 81.3g/L, the mass concentration of Fe 2+ is 4.56g/L, and the mass concentration of Al 3+ is 4.23g/L) Add waste liquid containing Cr 6+ to the mixture, oxidize Fe 2+ to Fe 3+ through oxidation-reduction reaction, and reduce Cr 6+ to Cr 3+ at the same time, until the chromium, iron, and aluminum elements in the mixed solution are only composed of Cr Exist in the form of 3+ , Fe 3+ , Al 3+ ;
(2)向步骤(1)中的混合溶液中加入饱和氢氧化钾溶液,直至pH=3.0,按照n(PO4 3-):n(Fe3++Al3+)=0.7:1的摩尔比,加入磷酸钾,并在60℃条件下保温搅拌40min,搅拌线速度控制在200m/min,过滤得到以磷酸铁为主的磷酸铁铝复合沉淀和滤液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为80.6g/L、0.42g/L、2.24g/L;(2) Add saturated potassium hydroxide solution to the mixed solution in step (1) until pH=3.0, according to the mole of n(PO 4 3- ):n(Fe 3+ +Al 3+ )=0.7:1 Add potassium phosphate, keep stirring at 60°C for 40 minutes, control the stirring line speed at 200m/min, filter to obtain iron-aluminum phosphate composite precipitation and filtrate mainly composed of iron phosphate; after testing, Cr 3+ , The mass concentrations of Fe 3+ and Al 3+ are 80.6g/L, 0.42g/L and 2.24g/L respectively;
(3)向步骤(2)中的滤液中加入饱和氢氧化钾溶液,直至pH=4.0,按照n(PO4 3-):n(Al3+)=1.2:1的摩尔比,加入磷酸钾,并在60℃条件下保温搅拌40min,搅拌线速度控制在200m/min,过滤得到以磷酸铝为主的磷酸铁铝复合沉淀和硫酸铬溶液;经检测,滤液中Cr3+、Fe3+、Al3+的质量浓度分别为79.6g/L、0.01g/L、0.246g/L。(3) Add saturated potassium hydroxide solution to the filtrate in step (2) until pH=4.0, according to the molar ratio of n(PO 4 3- ):n(Al 3+ )=1.2:1, add potassium phosphate , and kept stirring at 60°C for 40 minutes, the stirring line speed was controlled at 200m/min, and filtered to obtain iron-aluminum phosphate composite precipitation and chromium sulfate solution mainly composed of aluminum phosphate; after testing, Cr 3+ and Fe 3+ in the filtrate , Al 3+ mass concentrations are 79.6g/L, 0.01g/L, 0.246g/L respectively.
经过上述3步操作,含铬铁铝的硫酸体系溶液中的铬和铁铝实现了有效分离,其中铬元素主要以硫酸铬形式溶解在溶液中,铬回收率为97.92%;铁元素主要通过以磷酸铁为主的磷酸铁铝复合沉淀得以回收,铁回收率为99.78%;铝元素主要通过以磷酸铝为主的磷酸铁铝复合沉淀得以回收,铝回收率为94.18%。After the above three steps, the chromium and iron-aluminum in the sulfuric acid system solution containing chromium-iron-aluminum have been effectively separated, wherein the chromium element is mainly dissolved in the solution in the form of chromium sulfate, and the chromium recovery rate is 97.92%; The iron-aluminum phosphate composite precipitation mainly composed of iron phosphate can be recovered, and the iron recovery rate is 99.78%; the aluminum element is mainly recovered through the iron-aluminum phosphate composite precipitation mainly composed of aluminum phosphate, and the aluminum recovery rate is 94.18%.
上述实施例仅用于解释和说明本发明的具体实施方案,而并不旨在限制本发明的保护范围。应当理解的是,任何熟悉本技术领域的技术人员在本发明所披露的技术范围之内做出的修改或替换都应涵盖在本发明的保护范围之内。The above examples are only used to explain and illustrate the specific implementation of the present invention, and are not intended to limit the protection scope of the present invention. It should be understood that any modification or replacement made by those skilled in the art within the technical scope disclosed in the present invention shall fall within the protection scope of the present invention.
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