WO2012019265A1 - Processo para tratamento de efluentes líquidos e recuperação de metais - Google Patents

Processo para tratamento de efluentes líquidos e recuperação de metais Download PDF

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Publication number
WO2012019265A1
WO2012019265A1 PCT/BR2011/000274 BR2011000274W WO2012019265A1 WO 2012019265 A1 WO2012019265 A1 WO 2012019265A1 BR 2011000274 W BR2011000274 W BR 2011000274W WO 2012019265 A1 WO2012019265 A1 WO 2012019265A1
Authority
WO
WIPO (PCT)
Prior art keywords
amine
liquid
magnesium
effluents
recovering metals
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.)
Ceased
Application number
PCT/BR2011/000274
Other languages
English (en)
French (fr)
Portuguese (pt)
Inventor
Salomão Solino EVELIN
Roberto Mattioli Silva
Geraldo Luiz Da Silva
Clauson De Souza
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Vale SA
Original Assignee
Vale SA
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Family has litigation
First worldwide family litigation filed litigation Critical https://patents.darts-ip.com/?family=45567221&utm_source=google_patent&utm_medium=platform_link&utm_campaign=public_patent_search&patent=WO2012019265(A1) "Global patent litigation dataset” by Darts-ip is licensed under a Creative Commons Attribution 4.0 International License.
Priority to KR1020137005206A priority Critical patent/KR101843598B1/ko
Application filed by Vale SA filed Critical Vale SA
Priority to AU2011288945A priority patent/AU2011288945B2/en
Priority to PH1/2013/500273A priority patent/PH12013500273A1/en
Priority to CN201180043673.XA priority patent/CN103097558B/zh
Priority to CA2811452A priority patent/CA2811452C/en
Priority to EP11815938.3A priority patent/EP2604712B1/en
Priority to MX2013001599A priority patent/MX2013001599A/es
Priority to JP2013523444A priority patent/JP5752794B2/ja
Priority to US13/816,205 priority patent/US9410223B2/en
Priority to EA201390226A priority patent/EA023878B1/ru
Publication of WO2012019265A1 publication Critical patent/WO2012019265A1/pt
Anticipated expiration legal-status Critical
Priority to ZA2013/01249A priority patent/ZA201301249B/en
Ceased legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • C22B3/44Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/62Heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B26/00Obtaining alkali, alkaline earth metals or magnesium
    • C22B26/20Obtaining alkaline earth metals or magnesium
    • C22B26/22Obtaining magnesium
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B3/00Extraction of metal compounds from ores or concentrates by wet processes
    • C22B3/20Treatment or purification of solutions, e.g. obtained by leaching
    • C22B3/22Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/20Treatment of water, waste water, or sewage by degassing, i.e. liberation of dissolved gases
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5272Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using specific organic precipitants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Definitions

  • the process for producing nickel by the HPAL route consists essentially of the following steps: (i) preparation of nickel lateritic ore, (ii) nickel leaching under sulfuric acid pressure, (iii) nickel precipitation, (iv) re-leaching, (v) solvent extraction of nickel and (vi) electro-refining to produce nickel cathode (99.95% pure nickel metal) . Due to the significant presence of cobalt in the ore, it will be obtained as a co-product, also in metallic form.
  • the extraction levels of this process reach values from 92 to 96% for nickel and 90 to 92% for cobalt. Normally, to obtain this degree of extraction, the reaction suspension after chemical attack should have a residual free acid concentration of 30 to 50 g / L.
  • step (b) solid / liquid separation of the metal sulfides obtained in step (b) and formation of a metal free liquid phase;
  • the process object of the present invention further includes the following steps: d) addition of amine - in solution and in the proportion of 50 to 250 g / l - to the liquid phase, with precipitation of magnesium in the form of hydroxide - Mg (OH) 2; and e) amine recovery by depletion and rectification.
  • Figure 2 is a flow chart of the process for treating liquid effluents and recovering metals object of the present invention.
  • the process object of this invention also makes it possible to remove remaining metals in the liquid effluent such as manganese (Mn), zinc (Zn), cobalt (Co), copper (Cu), among others, thus creating conditions for their complete recycling in the wastewater. process, as well as providing additional micronutrient production for agricultural applications, among others.
  • Mn manganese
  • Zn zinc
  • Co cobalt
  • Cu copper
  • liquid effluent 1 is received in agitated tanks for equalization.
  • the homogenized (equalized) effluent 2 receives sulfide additions 3, in the form of Na 2 S and / or H 2 S, for precipitation of the remaining metals such as Ni, Co, Mn, Zn, Cu, among others. 4.
  • sulfides are subjected to a solid-liquid separation operation, resulting in a rich stream of metal sulfides. 5.
  • the sulfides are oxidized in stirred reactors with oxygen injection. 6 and The resulting solution 7 is crystallized to obtain the respective fractionated or mixed salts 8 which are stored and sent for dispatch 9.
  • the substantially metal-free liquid phase or effluent thus treated is transferred to the stirred reaction system, where it is contacted with low boiling amines via recovered amine 12 and replacement amine streams. 11, resulting from this reaction a suspension of precipitated magnesium hydroxide 13.
  • the amine is added at a rate of 50 to 250 g / l at a temperature of 25 to 70 ° C, solids content of 1 to 10% w / p, residence time 0.5 to 2 hours and suspension recycle ratio 5 to 40: 1.
  • this cake is subjected to drying and calcination, resulting in the obtaining of magnesia 17, which is stored, being part recycled to the nickel extraction process and the remainder traded 18.
  • the amine / effluent ratio It must be kept in the range of 100 to 200 g / L and is optimized according to the magnesium content in solution.
  • Part of the suspension of precipitated magnesium hydroxide is recirculated from the thickener underflow to the contact reactors in order to promote the growth of Mg (OH) 2 crystals through seeds.
  • the gaseous streams exiting the precipitation reactors and drying of magnesium hydroxide are transferred to an amine absorption system and returned to reprocessing the precipitation reactors.
  • the supernatant liquid phase of thickener 19 proceeds to the amine recovery step via distillation in two steps by depletion and then by rectification.
  • the depletion of the amine is effected by heating the amine-containing weak acid solution 19 to temperatures in the range 90 to 120 ° C with low pressure steam 27 - 1.5 to 3.0 kgf / cm 2 (man.) - fed continuously. This results in a tower bottom mass stream 21 consisting of weak acid and traces of amine, which is transferred to activated carbon columns to remove residual amounts of amine contained. The resulting weak acid 22 is transferred to the storage area, thereafter 23 for reuse in the hydrometallurgical process. Saturated activated carbon 24 proceeds to the regeneration step, after which 25 is recomposed with the addition of new carbon 26.
  • the amine recovery tests were performed in a laboratory distiller, coupled to a reactor-crystallizer, with the purpose of recycling the amine by fractional distillation and recovery of Mg (OH) 2.
  • the reactor was heated by a thermostated bath at 70 ° C.
  • a coil capacitor was connected to the reactor.
  • the condenser jacket was fed with water at 60 ° C and circulated by means of a peristaltic pump to keep the temperature constant.
  • the amine gas proceeded to bubbling in H 2 SO 4 solution (10% w / w).
  • the acid solution, receptor of all recovered amine was later analyzed to calculate the recovery of the organic reagent.
  • an inflated air stream was used into the reactor.
  • the pH of the solution was monitored throughout the experiment using a fingerprint meter.
  • Table 3 shows the evolution of liquid effluent quality during the treatment process object of this invention.
  • Mg is recovered as precipitated magnesium hydroxide, which can be easily recycled to earlier process steps as a low-cost alternative to state-of-the-art techniques. art.
  • sulfur is recovered in acidic water from the polishing operation on the coal columns.
  • the amine evaporates at lower temperatures, allowing the magnesium and sulfur recovered in this process step to be recirculated for the leaching operation.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Geology (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Removal Of Specific Substances (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
PCT/BR2011/000274 2010-08-09 2011-08-09 Processo para tratamento de efluentes líquidos e recuperação de metais Ceased WO2012019265A1 (pt)

Priority Applications (11)

Application Number Priority Date Filing Date Title
MX2013001599A MX2013001599A (es) 2010-08-09 2011-08-09 Proceso para tratar efluentes liquidos y recuperacion de metales.
EP11815938.3A EP2604712B1 (en) 2010-08-09 2011-08-09 A method for treating liquid effluents and recovering metals
AU2011288945A AU2011288945B2 (en) 2010-08-09 2011-08-09 A method for treating liquid effluents and recovering metals
PH1/2013/500273A PH12013500273A1 (en) 2010-08-09 2011-08-09 A method for treating liquid effluents and recovering metals
CN201180043673.XA CN103097558B (zh) 2010-08-09 2011-08-09 用于处理液体流出物和回收金属的方法
CA2811452A CA2811452C (en) 2010-08-09 2011-08-09 A process for treating liquid effluents and recovering metals
JP2013523444A JP5752794B2 (ja) 2010-08-09 2011-08-09 液体排出物の処理および金属の回収方法
KR1020137005206A KR101843598B1 (ko) 2010-08-09 2011-08-09 액체 배출물을 처리하고 금속을 회수하기 위한 방법
EA201390226A EA023878B1 (ru) 2010-08-09 2011-08-09 Способ проведения обработки жидких выходных потоков из технологических процессов и извлечения металлов
US13/816,205 US9410223B2 (en) 2010-08-09 2011-08-09 Process for treating liquid effluents and recovering metals
ZA2013/01249A ZA201301249B (en) 2010-08-09 2013-02-18 A method for teating liquid effluents and recovering metals

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
BRPI1003193-6A BRPI1003193B1 (pt) 2010-08-09 2010-08-09 processo para tratamento de efluentes líquidos e recuperação de metais
BRPI1003193-6 2010-08-09

Publications (1)

Publication Number Publication Date
WO2012019265A1 true WO2012019265A1 (pt) 2012-02-16

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ID=45567221

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/BR2011/000274 Ceased WO2012019265A1 (pt) 2010-08-09 2011-08-09 Processo para tratamento de efluentes líquidos e recuperação de metais

Country Status (15)

Country Link
US (1) US9410223B2 (enExample)
EP (1) EP2604712B1 (enExample)
JP (1) JP5752794B2 (enExample)
KR (1) KR101843598B1 (enExample)
CN (1) CN103097558B (enExample)
AU (1) AU2011288945B2 (enExample)
BR (1) BRPI1003193B1 (enExample)
CA (1) CA2811452C (enExample)
CL (1) CL2013000410A1 (enExample)
EA (1) EA023878B1 (enExample)
MX (1) MX2013001599A (enExample)
PE (1) PE20131206A1 (enExample)
PH (1) PH12013500273A1 (enExample)
WO (1) WO2012019265A1 (enExample)
ZA (1) ZA201301249B (enExample)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108178372A (zh) * 2017-12-29 2018-06-19 攀枝花钢企欣宇化工有限公司 一种除去氯化尾气吸收废盐中钒的方法

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104372377B (zh) * 2014-10-23 2017-04-05 云南煜锜环保科技有限公司 一种锌电解液中锌镁的循环蒸发结晶分离方法
CN110697998B (zh) * 2019-11-12 2022-04-22 东江环保股份有限公司 氧化铜生产废水的处理方法
CN113046574B (zh) * 2021-03-17 2022-07-29 沈阳有色金属研究院有限公司 一种利用铜电解脱铜后液处理粗氢氧化钴制备高纯镍、钴产品的方法
CN116926327A (zh) * 2022-03-31 2023-10-24 杜邦电子公司 一种从铜化学机械抛光的废料流中回收水和铜的方法

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1520175A (en) 1975-04-02 1978-08-02 Inco Ltd Process for the recovery of metals from solution
US20060228279A1 (en) * 2005-04-07 2006-10-12 Finlay Campbell Process for recovery of nickel and cobalt from laterite ore
US20070212765A1 (en) * 2006-03-08 2007-09-13 Purac Biochem B.V. Method for preparing an organic amine
US20090148366A1 (en) 2005-12-22 2009-06-11 Eric Girvan Roche Magnesium Oxide Recovery
US20090180945A1 (en) 2008-01-15 2009-07-16 Vale Inco Limited Liquid and solid effluent treatment process

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US5587088A (en) * 1995-08-01 1996-12-24 Bader; Mansour S. Precipitation and separation of inorganic species from aqueous solutions
JP3780356B2 (ja) * 1999-12-28 2006-05-31 太平洋セメント株式会社 石油系燃焼灰の処理方法
US7392848B1 (en) * 2005-05-27 2008-07-01 Bader Mansour S Methods to produce sulfate-free saline water and gypsum
CN100392124C (zh) * 2006-08-25 2008-06-04 四川大学 从高镁磷矿中回收镁的工艺方法

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1520175A (en) 1975-04-02 1978-08-02 Inco Ltd Process for the recovery of metals from solution
US20060228279A1 (en) * 2005-04-07 2006-10-12 Finlay Campbell Process for recovery of nickel and cobalt from laterite ore
US20090148366A1 (en) 2005-12-22 2009-06-11 Eric Girvan Roche Magnesium Oxide Recovery
US20070212765A1 (en) * 2006-03-08 2007-09-13 Purac Biochem B.V. Method for preparing an organic amine
US20090180945A1 (en) 2008-01-15 2009-07-16 Vale Inco Limited Liquid and solid effluent treatment process
WO2009089613A1 (en) * 2008-01-15 2009-07-23 Vale Inco Limited Liquid and solid effluent treatment process

Non-Patent Citations (1)

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Title
See also references of EP2604712A4

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108178372A (zh) * 2017-12-29 2018-06-19 攀枝花钢企欣宇化工有限公司 一种除去氯化尾气吸收废盐中钒的方法

Also Published As

Publication number Publication date
US9410223B2 (en) 2016-08-09
AU2011288945B2 (en) 2015-05-14
AU2011288945A1 (en) 2013-03-28
CA2811452A1 (en) 2012-02-16
CN103097558A (zh) 2013-05-08
BRPI1003193A2 (pt) 2012-05-02
KR101843598B1 (ko) 2018-03-29
MX2013001599A (es) 2013-10-28
CL2013000410A1 (es) 2013-09-06
EA201390226A1 (ru) 2013-08-30
JP5752794B2 (ja) 2015-07-22
CA2811452C (en) 2018-01-02
BRPI1003193B1 (pt) 2019-09-10
US20130343972A1 (en) 2013-12-26
EP2604712B1 (en) 2017-10-11
JP2013540889A (ja) 2013-11-07
PH12013500273A1 (en) 2017-08-23
ZA201301249B (en) 2014-02-26
EP2604712A1 (en) 2013-06-19
EP2604712A4 (en) 2014-11-19
EA023878B1 (ru) 2016-07-29
KR20130136972A (ko) 2013-12-13
CN103097558B (zh) 2015-04-29
PE20131206A1 (es) 2013-10-13

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