CN101886179B - Method for separating ferrum, copper and silicon components from copper smelting residues - Google Patents

Method for separating ferrum, copper and silicon components from copper smelting residues Download PDF

Info

Publication number
CN101886179B
CN101886179B CN2010102237032A CN201010223703A CN101886179B CN 101886179 B CN101886179 B CN 101886179B CN 2010102237032 A CN2010102237032 A CN 2010102237032A CN 201010223703 A CN201010223703 A CN 201010223703A CN 101886179 B CN101886179 B CN 101886179B
Authority
CN
China
Prior art keywords
copper
alkali
acid
residues
copper smelting
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.)
Expired - Fee Related
Application number
CN2010102237032A
Other languages
Chinese (zh)
Other versions
CN101886179A (en
Inventor
陈茂生
韩子荣
陈锦
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.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
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
Application filed by Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CN2010102237032A priority Critical patent/CN101886179B/en
Publication of CN101886179A publication Critical patent/CN101886179A/en
Application granted granted Critical
Publication of CN101886179B publication Critical patent/CN101886179B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a method for separating components, i.e. ferrum, copper, silicon, and the like, from copper smelting waste residues, which comprehensively recovers Si, Cu, Fe, and the like contained in the copper residues by using the copper smelting waste residues as raw materials and adopting thermal chemical reaction, water leaching and acid leaching or the conventional beneficiation technology so as to realize the resource recycling of the copper smelting waste residues. The method comprises the following steps of: mainly mixing alkali and the copper smelting waste residues according to a certain proportion to carry out heating reaction; selecting residue-alkali ratio, heating temperature and heat reaction time according to copper residue composition, and then firstly separating silicon dioxide entering a liquid phase in terms of sodium (potassium) silicate through the water leaching, filtering and washing; carrying out further acid (hydrochloric acid or sulfuric acid) adding treatment on a silicate solution so as to obtain a finished product of white carbon black through sedimentation, filtering and the drying of filter residues; concentrating filter liquor so as to obtain a saturated sodium (potassium) chloride/sodium (potassium) sulfate solution (recycled for recycling in an alkali industry); and further separating water leaching residues through acid leaching or the conventional beneficiation method so as to recover copper, ferrum, and the like.

Description

The method of separating ferrum, copper, silicon components from copper smelting slag
Technical field
The present invention relates to the metal metallurgy smelting production field, particularly relate to copper smelting slag application technology as the second resource processing method.
Background technology
Copper slag is mainly derived from pyrometallurgical smelting process, such as reverberatory smelting, Flash Smelting Furnace melting, Noranda process, Ai Safa, electric furnace etc.According to statistics, the annual copper ashes quantum of output of China is more than 8,000,000 tons.Because production technique is different, the Chemical Composition of copper ashes also has different, all contains a large amount of valuable metal element, especially SiO in the copper ashes 2(W SiO2=22~40%), Cu (W Cu=0.5~5% and Fe (W Fe22~63%).And the phase in the copper ashes is mainly fayalite, the glassiness, ferriferous oxide, copper matte regulus (Cu 2The S-FeS Solid solution) metallic iron of feldspar and minute quantity and metallic copper etc.Existing main methods is that these waste residues are directly stacked, and has so namely taken the soil, has caused again significant wastage and the environmental pollution of the resources such as copper, silicon, iron.At present both at home and abroad the method processed of copper ashes mainly contain pyrogenic process dilution (such as reverberatory furnace dilution, electric furnace process etc.), beneficiating method, wet-leaching (comprise direct leaching, indirectly leach and Bioleaching) and the hot method of pyrocarbon, only can reclaim in the copper ashes than small part Fe and Cu, the rate of recovery is lower, cost recovery is higher, and the recycling rate is extremely low.In addition, because copper ashes has good physical and mechanical properties, for the production of irony cement, abrasive material tools or as pavior, caused the resource serious waste on a small quantity.Under the severe situation of China's existing resource scarcity, exploitation copper ashes comprehensive utilization of resources technology has important strategic importance and realistic meaning to promoting recycling economy and Sustainable development and environment protection.
The maximum difficult point that exists at present: copper, iron in the copper ashes, the silicon mosaic granularity is superfine and be evenly distributed, and multi mineral is wrapped up mutually, makes hard, the stable chemical nature of its compact structure, and prior art is difficult to separate, and the recycling rate is extremely low.In addition, be with ferrosilicate, martial ethiops, fayalite (2FeOSiO 2), magnetite (Fe 3O 4) and the amorphous glass body that forms of some gangues.The fayalite proportion of weak magnetic is larger, and the magnetic method divided silicon can't be realized, has limited its direct application in ironmaking production, thereby has caused the significant wastage of iron resources.Moreover surperficial quasi-vitreous, beneficiation reagent are difficult to be applied to the wherein copper of parcel, cause existing beneficiation method effectiveness lower.
Summary of the invention
Problem for above-mentioned prior art existence, the present invention proposes Fe, the Cu in employing thermal chemical reaction, water logging and acidleach or the conventional beneficiation method Recovering Copper slag, Si etc. take copper smelting slag as raw material, copper ashes and alkali are mixed in proportion, get final product through reacting by heating, water logging, filtration, selective separation, then the method for separating ferrum, copper, silicon components from copper smelting slag.
The present invention a kind of from copper smelting slag the method for separating ferrum, copper, silicon components, it is characterized in that Fe, Cu, Si in employing thermal chemical reaction, water logging and acidleach or the conventional beneficiation method Recovering Copper slag take copper smelting slag as raw material, copper ashes and alkali are mixed in proportion, through reacting by heating, water logging, filtration, selective separation.
Concrete technology may further comprise the steps: copper ashes and alkali are mixed in proportion, and the reacting by heating temperature is controlled between 350-950 ℃, and slag alkali is than control 1: 0.37~2.6, and the reaction times is 0.3-5.0 hour; Then adopt water logging, get after filtration filtrate and filter residue; Filtrate is sodium silicate solution, and filtrate is by acid adding, and pH=3-6 is controlled in neutralization, and through precipitation, filtration, washing, the filter residue drying can obtain the finished product white carbon black; Concentrating filter liquor can make saturated sodium-chloride or Repone K/sodium sulfate or potassium sulfate solution; Fe, Cu enter filter residue after the water logging, and filter residue is through being recyclable copper, iron by acidleach or conventional beneficiation method further.
Described copper ashes is milled to the following or direct hot melt of 1.0mm.
The alkali of described copper ashes and alkali is KOH, NaOH or Na 2CO 3
Described filtrate is hydrochloric acid or sulfuric acid by the acid of acid adding.
The present technique method compared with prior art has following features:
1, present technique has comprehensive utilization of resources rate height, tooling cost is low, technical process is short, added value of product is high; The silicon dioxide rate of recovery 〉=90%, copper recovery 〉=85%, iron recovery 〉=85%.
2, treating processes non-wastewater discharge, processing wastewater can be realized zero release.
3, treating processes produces without solid waste, and the solid waste comprehensive utilization ratio reaches 100%.
4, can effectively utilize the deslagging waste heat, realize energy-saving and emission-reduction.
Description of drawings
Fig. 1 production process route figure of the present invention.
Embodiment
Further specify flesh and blood of the present invention below in conjunction with accompanying drawing with example, but content of the present invention is not limited to this.
Main technique of the present invention may further comprise the steps: with copper ashes and alkali (KOH, NaOH, Na 2CO 3) mix by a certain percentage; The reacting by heating temperature is controlled between 350-950 ℃, slag alkali mass ratio control 1: 0.37~2.6, and the reaction times is 0.3-5.0 hour; Then adopt water logging, get after filtration filtrate and filter residue, filtrate is water glass (potassium) solution, and Fe, Cu etc. enters filter residue.Filtrate is by acid adding (hydrochloric acid or sulfuric acid) neutralization control pH=3-6, and through precipitation, filtration, the filter residue drying can obtain the finished product white carbon black; Concentrating filter liquor can make saturated sodium-chloride (potassium)/sodium sulfate (potassium) solution.The filter residue that obtains after the water logging is through being recyclable copper, iron etc. by acidleach or conventional beneficiation method further.
Embodiment 1: copper ashes is milled to weigh below the 1.0mm 40g and sodium hydroxide mixes at 1: 0.37 by slag alkali weight ratio, place retort furnace to be heated to 550 ℃, constant temperature 3 hours, take out when treating that temperature is down to 150 ℃ of left and right sides and place hot water (400ml) to carry out water logging (2 hours), through precipitation, solid-liquid separation.Filter cake is washed twice and is carried out acidleach with dilute sulphuric acid and carry copper (make copper-bath, copper recovery is 85%) afterwards; Again after filtration, wash, dry and to get iron oxide product (iron recovery is 92%).Water logging filtered liquid acid neutralization is regulated pH=4.5, and through precipitation, solid-liquid separation, filter cake washes twice, and the filter cake drying gets finished product white carbon black (the silicon rate of recovery reaches 92%); Concentrating filter liquor is to the saturated sodium chloride saturated solution product that gets.
Embodiment 2: copper ashes is milled to the 40g that weighs below the 0.6mm, mix at 1: 2.5 by slag alkali weight ratio with sodium hydroxide, place retort furnace to be heated to 350 ℃, isothermal reaction 2 hours, take out when treating that temperature is down to 150 ℃ of left and right sides and place hot water (400ml) to carry out water logging (1 hour), through precipitation, solid-liquid separation; Filter cake is washed twice and is carried out acidleach with dilute sulphuric acid and carry copper (make copper-bath, copper recovery is 90%) afterwards, refilters, dries and to get iron oxide product, and iron recovery is 95%.Water logging filtrate adds in the hydrochloric acid and regulates pH=3, and through solid-liquid separation, filter cake washes twice, and the filter cake drying gets finished product white carbon black (the silicon rate of recovery reaches 96%); Concentrating filter liquor is to the saturated sodium chloride saturated solution product that gets.
Embodiment 3: with the powdery copper ashes 40g that weighs, mix at 1: 0.6 by slag alkali weight ratio with potassium hydroxide, place retort furnace to be heated to 500 ℃, constant temperature 3 hours, take out when treating that temperature is down to 200 ℃ of left and right sides and place hot water (400ml) to carry out water logging (2 hours), through precipitation, solid-liquid separation; Filter cake is washed twice and is carried out acidleach with dilute sulphuric acid and carry copper (make copper-bath, copper recovery is 88%) afterwards, refilters, dries to such an extent that the iron oxide product iron recovery is 95%.Filtrate adds in the hydrochloric acid and regulates pH value to 6, and through solid-liquid separation, filter cake washes twice, and the filter cake drying gets finished product white carbon black (the silicon rate of recovery reaches 94%); Concentrating filter liquor is to the saturated saturated potassium chloride solution product that gets.
Embodiment 4: copper ashes is milled to weigh below the 0.6mm 40g and yellow soda ash mixes at 1: 2.6 by slag alkali weight ratio, place retort furnace to be heated to 850 ℃, constant temperature 1 hour, take out when treating that temperature is down to 150 ℃ of left and right sides and place hot water (400ml) to carry out water logging (5 hours), precipitation, solid-liquid separation.Filter cake washes twice, and ferric oxide (rate of recovery is 85%) is isolated in dry, broken, magnetic separation, and the recovery of copper rate is 87%; Add salt acid for adjusting pH value to 5 in the filtrate, precipitation, solid-liquid separation, filter cake washes twice, and the filter cake drying gets white carbon black (the silicon rate of recovery reaches 95%); Concentrating filter liquor is to the saturated sodium chloride saturated solution product that gets.
Embodiment 5: the copper ashes 40g that weighs is put into reactor and is heated to 950 ℃, sodium hydroxide is by the slag alkali weight ratio heat fused of weighing at 1: 1, then slag is slowly inserted in the sodium hydroxide molten bath of fusing, after 18 minutes kinds of question response, place hot water (500ml) to carry out water logging (3 hours), through precipitation, solid-liquid separation.Filter cake is washed twice and is carried out acidleach with dilute sulphuric acid and carry copper (make copper-bath, copper recovery is 91%) afterwards, refilters, dries and to get iron oxide product, and iron recovery is 96%.The water logging filtered liquid adds in the sulfuric acid and regulates pH=4, and through solid-liquid separation, filter cake washes twice, and the filter cake drying gets finished product white carbon black (the silicon rate of recovery reaches 93%); Concentrating filter liquor is to the saturated sodium sulfate saturated solution product that gets.

Claims (4)

1. the method for a separating ferrum from copper smelting slag, copper, silicon components, it is characterized in that: adopt Fe, Cu, Si in thermal chemical reaction, water logging and the conventional beneficiation method Recovering Copper slag take copper smelting slag as raw material, copper ashes and alkali are mixed in proportion, through reacting by heating, water logging, filtration, selective separation;
Concrete technology may further comprise the steps: copper ashes and alkali are mixed in proportion, and the reacting by heating temperature is controlled between 350 ℃~950 ℃, and slag alkali is than control 1: 0.37~2.6, and the reaction times is 0.3~5.0 hour; Then adopt water logging, get after filtration filtrate and filter residue; Filtrate is water glass or potassium silicate solution, and filtrate is by acid adding, and pH=3~6 are controlled in neutralization, and through precipitation, filtration, washing, the filter residue drying can obtain the finished product white carbon black; Concentrating filter liquor can make saturated sodium-chloride or Repone K/sodium sulfate or potassium sulfate solution; Fe, Cu enter filter residue after the water logging, and filter residue is through being recyclable copper, iron by conventional beneficiation method further.
As claimed in claim 1 from copper smelting slag the method for separating ferrum, copper, silicon components, it is characterized in that: described copper ashes is milled to the following or direct hot melt of 1.0mm.
As claimed in claim 1 from copper smelting slag the method for separating ferrum, copper, silicon components, it is characterized in that: the alkali of described copper ashes and alkali is KOH, NaOH or Na 2CO 3
As claimed in claim 1 from copper smelting slag the method for separating ferrum, copper, silicon components, it is characterized in that: described filtrate is hydrochloric acid or sulfuric acid by the acid of acid adding.
CN2010102237032A 2010-07-12 2010-07-12 Method for separating ferrum, copper and silicon components from copper smelting residues Expired - Fee Related CN101886179B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2010102237032A CN101886179B (en) 2010-07-12 2010-07-12 Method for separating ferrum, copper and silicon components from copper smelting residues

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2010102237032A CN101886179B (en) 2010-07-12 2010-07-12 Method for separating ferrum, copper and silicon components from copper smelting residues

Publications (2)

Publication Number Publication Date
CN101886179A CN101886179A (en) 2010-11-17
CN101886179B true CN101886179B (en) 2013-03-06

Family

ID=43072269

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2010102237032A Expired - Fee Related CN101886179B (en) 2010-07-12 2010-07-12 Method for separating ferrum, copper and silicon components from copper smelting residues

Country Status (1)

Country Link
CN (1) CN101886179B (en)

Families Citing this family (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102294297B (en) * 2011-09-16 2013-01-02 大冶有色金属股份有限公司 Magnetic suspension beneficiation combined method for recycling copper from copper melting converter slag
CN102559958A (en) * 2012-02-20 2012-07-11 武汉科技大学 Method for improving grindability of metallurgical slag
CN102534236A (en) * 2012-02-20 2012-07-04 武汉科技大学 Method for recovering valuable metal from metallurgical slag materials
CN103882235B (en) * 2014-04-15 2015-08-19 中国地质科学院矿产综合利用研究所 Method for step recovery of iron, copper and noble metal from copper smelting waste slag
CN105506297A (en) * 2015-12-10 2016-04-20 中南大学 Resource utilization method for copper smelting slag
CN105483363A (en) * 2015-12-10 2016-04-13 中南大学 Method for co-production of activated calcium silicate by adopting copper tailings to produce iron ore concentrate
CN106242007A (en) * 2016-07-25 2016-12-21 江苏星鑫分离设备制造有限公司 A kind of preparation method of copper-containing residue solid ozone Composite denitrification agent
CN107746058A (en) * 2017-10-19 2018-03-02 玉溪师范学院 A kind of method for efficiently producing silica dioxide gel using copper smelting slag
CN109112243B (en) * 2018-09-06 2020-04-24 钢研晟华科技股份有限公司 Method for preparing metallic iron by using copper slag
CN109437619B (en) * 2018-12-04 2021-08-20 上海中冶环境工程科技有限公司 Application of smelting copper slag as cement iron correction agent and cement
CN112695203A (en) * 2020-12-07 2021-04-23 鹰潭盛发铜业有限公司 Efficient and environment-friendly recovery method of copper slag
CN112591757A (en) * 2021-01-04 2021-04-02 南京工大环境科技有限公司 Method for preparing white carbon black and sponge copper from organic silicon slurry residues
CN113120911B (en) * 2021-04-20 2023-09-12 昆明理工大学 Method for ultrasonically reinforcing and separating silicon and iron in copper smelting slag and preparing white carbon black by utilizing silicon

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101100708A (en) * 2006-07-07 2008-01-09 隋智通 Method for separating iron and copper from copper smelt slag
CN101555551A (en) * 2009-05-22 2009-10-14 昆明理工大学 Method for comprehensively recovering Fe, Cu and Si from copper smelting slag

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
BG66201B1 (en) * 2008-09-23 2012-01-31 Георги ГЮРОВ METHOD FOR RECYCLING OF HONEY FROM COPPER PRODUCTION

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101100708A (en) * 2006-07-07 2008-01-09 隋智通 Method for separating iron and copper from copper smelt slag
CN101555551A (en) * 2009-05-22 2009-10-14 昆明理工大学 Method for comprehensively recovering Fe, Cu and Si from copper smelting slag

Also Published As

Publication number Publication date
CN101886179A (en) 2010-11-17

Similar Documents

Publication Publication Date Title
CN101886179B (en) Method for separating ferrum, copper and silicon components from copper smelting residues
CN101555551B (en) Method for comprehensively recovering Fe, Cu and Si from copper smelting slag
CN102776376B (en) Method for recovering valuable metal from waste residue containing lead and zinc through wet-fire combination process
CN105293564A (en) Method for recycling zinc-containing dust ash in steel plant
CN105039699B (en) The solid fluorine reconstruct extraction alkali metal Slag treatment of lepidolite and resource utilization method
CN102363522B (en) Technology for extracting selenium from low-grade selenium-containing material
CN102134648B (en) Method for comprehensive treatment of industrial waste
CN101723713A (en) Overall treatment method of steel works sintering dust
CN106676281A (en) Process for comprehensively recycling copper and iron through ore phase restructuring of copper smelting molten slag
CN104342561A (en) Method for recovering copper, iron and silicon from copper smelting slag
CN103088208A (en) Method for treating manganese-containing and phosphorus-containing hematite
CN102212683A (en) Wet metallurgical method with comprehensive reclamation, basically no three wastes and zero discharge
CN103789553A (en) Method for comprehensively utilizing lepidolite mineralogical reconstruction lithium-extraction slags
CN104017991A (en) Process for efficiently and selectively separating copper in lead copper matte
CN106119556A (en) A kind of Application way of steel plant zinc smoke ash
CN104561551B (en) A kind of method of the valuable constituent element separation and Extraction of boron magnesium iron mineral intergrowth
CN103343225A (en) Comprehensive utilization method of ferriferous fayalite material
CN103757198B (en) Method for extracting high-purity pyrite and arsenopyrite from carlin-type gold deposit
CN101723439A (en) Method for recovering lead chloride from sintered ashes and preparing lead monoxide
CN103074484A (en) Comprehensive treatment method of oolitic hematite containing phosphorus and red mud
CN107723473A (en) Comprehensive utilization method of high-arsenic-content polymetallic gold ore
CN104846208B (en) Method for comprehensively recovering gold and silver in lead-silver slag
CN102242282B (en) Alkaline reduction smelting method for vanadium polymetallic ore
CN104789771B (en) Complicated copper-lead zinc-silver bulk concentrate valuable metal separation method
CN107326187B (en) A method of selective recovery zinc and iron from electric arc furnaces flue dust

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20130306

Termination date: 20150712

EXPY Termination of patent right or utility model