WO2012019265A1 - Processo para tratamento de efluentes líquidos e recuperação de metais - Google Patents
Processo para tratamento de efluentes líquidos e recuperação de metais Download PDFInfo
- 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
Links
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
-
- 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
- C22B3/44—Treatment or purification of solutions, e.g. obtained by leaching by chemical processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/62—Heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
- C22B23/00—Obtaining nickel or cobalt
-
- 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
- C22B26/00—Obtaining alkali, alkaline earth metals or magnesium
- C22B26/20—Obtaining alkaline earth metals or magnesium
- C22B26/22—Obtaining magnesium
-
- 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
- C22B3/22—Treatment or purification of solutions, e.g. obtained by leaching by physical processes, e.g. by filtration, by magnetic means, or by thermal decomposition
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/048—Purification of waste water by evaporation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/20—Treatment of water, waste water, or sewage by degassing, i.e. liberation of dissolved gases
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5272—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using specific organic precipitants
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/16—Nature 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
-
- 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
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)
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 |
Family
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)
| 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)
| 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)
| 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 |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| 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 |
-
2010
- 2010-08-09 BR BRPI1003193-6A patent/BRPI1003193B1/pt not_active IP Right Cessation
-
2011
- 2011-08-09 CN CN201180043673.XA patent/CN103097558B/zh not_active Expired - Fee Related
- 2011-08-09 PE PE2013000249A patent/PE20131206A1/es not_active Application Discontinuation
- 2011-08-09 US US13/816,205 patent/US9410223B2/en not_active Expired - Fee Related
- 2011-08-09 EA EA201390226A patent/EA023878B1/ru not_active IP Right Cessation
- 2011-08-09 WO PCT/BR2011/000274 patent/WO2012019265A1/pt not_active Ceased
- 2011-08-09 KR KR1020137005206A patent/KR101843598B1/ko not_active Expired - Fee Related
- 2011-08-09 AU AU2011288945A patent/AU2011288945B2/en not_active Ceased
- 2011-08-09 EP EP11815938.3A patent/EP2604712B1/en not_active Not-in-force
- 2011-08-09 JP JP2013523444A patent/JP5752794B2/ja not_active Expired - Fee Related
- 2011-08-09 MX MX2013001599A patent/MX2013001599A/es not_active Application Discontinuation
- 2011-08-09 PH PH1/2013/500273A patent/PH12013500273A1/en unknown
- 2011-08-09 CA CA2811452A patent/CA2811452C/en active Active
-
2013
- 2013-02-08 CL CL2013000410A patent/CL2013000410A1/es unknown
- 2013-02-18 ZA ZA2013/01249A patent/ZA201301249B/en unknown
Patent Citations (6)
| 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)
| Title |
|---|
| See also references of EP2604712A4 |
Cited By (1)
| 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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