CN105200172A - Synergistic processing method of stacked EAF stainless steel slag and LF refining slag - Google Patents

Synergistic processing method of stacked EAF stainless steel slag and LF refining slag Download PDF

Info

Publication number
CN105200172A
CN105200172A CN201510565156.9A CN201510565156A CN105200172A CN 105200172 A CN105200172 A CN 105200172A CN 201510565156 A CN201510565156 A CN 201510565156A CN 105200172 A CN105200172 A CN 105200172A
Authority
CN
China
Prior art keywords
slag
stainless steel
eaf
refining
steel slag
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.)
Granted
Application number
CN201510565156.9A
Other languages
Chinese (zh)
Other versions
CN105200172B (en
Inventor
李俊国
曾亚南
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.)
North China University of Science and Technology
Original Assignee
North China 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 North China University of Science and Technology filed Critical North China University of Science and Technology
Priority to CN201510565156.9A priority Critical patent/CN105200172B/en
Publication of CN105200172A publication Critical patent/CN105200172A/en
Application granted granted Critical
Publication of CN105200172B publication Critical patent/CN105200172B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies

Landscapes

  • Carbon Steel Or Casting Steel Manufacturing (AREA)
  • Processing Of Solid Wastes (AREA)
  • Furnace Details (AREA)

Abstract

The invention discloses a synergistic processing method of stacked EAF stainless steel slag and LF refining slag. The method comprises the following steps: uniformly mixing the stacked EAF stainless steel slag, the LF refining slag and coke powder and/or pulverized coal to form mixed slag, and then heating, cooling and post-processing the mixed slag to obtain the processed refined slag. Under the high temperature effect, carbon in the coke powder or pulverized coal is used for reducing Cr<6+> in the EAF stainless steel slag to Cr<3+>; by sufficiently utilizing the characteristic that the high content of Al2O3 in the LF refining slag facilitates the generation of spinel, the reduced Cr2O3 enters the spinel to be cured and sealed, the leaching concentration of Cr<6+> in the refining slag is several micrograms per liter and is far less than a standard limit value of the national standard dangerous waste identification standard leaching toxicity identification (GB5085.3-2007), the harmless treatment of the stacked EAF stainless steel slag is effectively realized, and the harmless treatment of the EAF stainless steel slag and synergistic treatment on the cold-state LF refining slag can be realized; the process is simple, the waste is treated by virtue of waste, and the harmless treatment cost is saved; the method has characteristics of energy conservation, environmental protection and good treatment effect.

Description

Store up the cooperative processing method of EAF stainless steel slag and LF refining slag
Technical field
The present invention relates to a kind for the treatment of process of slag, especially a kind of cooperative processing method storing up EAF stainless steel slag and LF refining slag.
Background technology
2014, Chinese stainless steel crude steel output was 2169.2 ten thousand tons, increases by 14.27% on a year-on-year basis.Produce 1 ton containing chromium refuse (mainly comprising stainless steel slag, acid-washing stainless steel mud etc.) by every 3 tons of stainless steels, exceed 7,000,000 tons containing chromium refuse year generation.At present, stainless steel main production equipments is electric furnace (ElectricArcFurnace, EAF) and argon oxygen decarburizing furnace (ArgonOxygenDecarburization, AOD), and therefore stainless steel slag mainly comprises EAF slag and AOD slag.Stainless steel slag principal element is Ca, Si, Mg, Al, Fe etc., but due to the heavy metal content such as Cr in stainless steel slag higher, its recycling must consider its pulverability, stability and leaching.Pulverability is mainly by oblique crystal β-C 2s is to octahedra γ-C 2s without about there being the volumetric expansion of 12% to cause in hot phase transition process; Stability by f-CaO and f-MgO hydrolytic process 97.8% and 148% volumetric expansion cause; Leaching refers to that stainless steel slag is stacked or tailings is used as after material of construction under the leaching liquor effects such as rainwater, and the toxic heavy metals such as Cr enter the ability of water body.Due to heavy metal leachings such as chromium, the comprehensive Utilization Ways of stainless steel slag is restricted, and on a small quantity for steel slag cement and material of construction preparation, and more stainless steel slags can only to store up process.
Because the melting later stage is reducing atmosphere, hypoxemia gesture controls the oxidation of metal and metalloid, therefore the Cr in EAF stainless steel slag mainly exists with metallic state and+3 valency forms, metallic state chromium usually and Ni, Fe form alloy, reclaimed by fine grinding and magnetic separation, and trivalent chromium is mainly present in Ca-Mg-Al silicate and spinels mineral.A lot of scholar thinks, not only the Cr in stainless steel slag when high temperature 3+cr can be oxidized to 6+, under normal temperature state, this reaction also possesses thermodynamical reaction condition, and after especially material absorbs moisture, CaO hydrolysis will generate the more Ca in oxygen center (OH) 2, make the Cr that oxytropism is stronger 3+more easily be oxidized to Cr 6+, thus increase the leaching toxicity of chromium in EAF stainless steel slag.Due to the impact by kinetic factor, EAF stainless steel slag stores up Cr after 1 year 3+oxidation ratio about 10%, greatly strengthen the leaching toxicity of EAF stainless steel slag.Therefore, rationally disposal is stored up for some time and is contained a certain amount of Cr 6+eAF stainless steel slag of storing up be disposal of waste gas, water and industrial residue field worker's issues that need special attention.At present, store up the harmless treatment of EAF stainless steel slag and mainly contain three classes:
(1) high temperature reduction method: pyrocarbon reduction is with coke, powdered carbon, wood chip, coal gangue and eutrophication algae slag etc. as reductive agent, and the excessive C that utilization wherein contains and stainless steel slag carry out high-temperature fusion reaction, by Cr in slag 6+be reduced to Cr 3+, finally exist with vitreous state or spinel, can be used as Product recycling and use.Except solid state reduction agent, the gases such as hydrogen, methane, carbon monoxide also can be adopted as reductive agent to Cr 3+reduce.It is not thorough often to there is reduction in solid phase high temperature reduction, and it is inflammable gas that gas phase high temperature reduction exists again reductive agent, technique relative complex, otherwise easily causes new pollution.
(2) wet reducing method: stainless steel slag mixes with acid or basic solution, and adds in solution containing the reducing substances such as ferrous sulfate, alkali metalsulphide, by Cr 6+be reduced to Cr 3+, and in basic solution Precipitation Cr (OH) 3with recycling use.Different according to reaction conditions, acidic reduction method, alkaline reduction method and organophosphorus waste liquid reduction method can be divided into.These methods need consumption acids alkaline solution, and produce new sewage need process.
(3) cement solidification method: by a certain amount of stainless steel ground-slag with addition of a certain amount of FeSO 4, FeCl 2deng adding cement clinker after additive, the mixing that adds water, stirring, shaping and solidify, along with aquation and the setting and harden process of cement, Cr is sealed in not stripping in hardening of cement body, reaches stable and innoxious object.Its shortcoming to be after cement solidification, due to the volumetric expansion of chromium slag, to cause cement and concrete stability.
LF refining has the metallurgical characteristics such as equipment is simple, investment cost is low, flexible operation, refining effect are good, is developed rapidly, become indispensable one critical process in modernization Iron and Steel Production short route as the effective means promoting steel metallurgical quality.In LF refining process, the feature of refining slag high alkalinity, low oxidative and high sulfur capacity is mainly utilized to carry out refining to molten steel, to realize steel liquid deoxidation, desulfurization, the metallurgical functions such as the form of the inclusion in absorption steel, control inclusion, improve molten steel cleanness.But, also produce a large amount of refining slag after refining, account for about 3% of output of steel.Produce 8.23 hundred million tons of steel per year according to 2014,1/2 calculates, then every year by generation 1,235 ten thousand tons of LF refining slags through LF refining.The direct discharge of a large amount of LF refining slag, by the waste of the severe contamination and resource that cause environment, does not meet green, ecological metallurgical demand for development.
At present, LF refining slag is recycled and is mainly contained hot Returning utilization and cold conditions process two kinds of techniques.Hot refining slag is mainly returned electric furnace or converter procedure by hot Returning utilization, lime desulfurization, dephosphorization is replaced to reduce the lime consumption of steel making working procedure, the heat of residue effectively recycled simultaneously, reduce steel making working procedure energy consumption, reduce pollution to environment; But due to the enrichment of sulphur, phosphorus content in slag, the number of times of hot refining slag cycling and reutilization is restricted.Cold conditions process returns blast furnace ironmaking or converter steelmaking by after cold conditions refining slag and the mixing of materials such as ferrous material, binding agent, coldmoulding; But this kind of method can only utilize the flux effect of refining slag, and processing rate is restricted.
Summary of the invention
The technical problem to be solved in the present invention be to provide a kind of effectively, the cooperative processing method storing up EAF stainless steel slag and LF refining slag of environmental protection.
For solving the problems of the technologies described above, the technical solution used in the present invention is: it will store up EAF stainless steel slag, LF refining slag, be mixed into coke powder and/or coal dust and mix slag, then mix slag after heating, cooling, aftertreatment, obtain the refining slag after processing.
In mixing slag of the present invention, the mass percentage of each material is: store up EAF stainless steel slag 3% ~ 10%, LF refining slag 88% ~ 96%, coke powder and/or coal dust 1% ~ 2%.
The present invention adopts microwave to heat.Described microwave power is 150W ~ 900W, and heat-up time is 30 ~ 90min.
The beneficial effect adopting technique scheme to produce is: the present invention utilizes the carbon in coke powder or coal dust to make to store up Cr in EAF stainless steel slag under high temperature action 6+be reduced to Cr 3+; Make full use of LF refining slag height Al 2o 3content is conducive to the feature that spinel generates, and makes the Cr of reduction 2o 3enter spinel be cured and seal up for safekeeping, the refining slag Cr after process 6+leaching concentration is a few microgram liters, far below the standard limited value in country " Hazardous wastes judging standard leaching characteristic identification " (GB5085.3-2007), have effectively achieved the harmless treatment of storing up EAF stainless steel slag, realize storing up the innoxious of EAF stainless steel slag and cold conditions LF refining slag associated treatment.Therefore, present invention process is simple, and the treatment of wastes with processes of wastes against one another, has saved harmless treatment cost; There is energy-conserving and environment-protective, feature that treatment effect is good.
When the present invention adopts microwave heating, make full use of the features such as microwave method heating is fast, hear rate is little, homogeneous heating, effectively can promote treatment effect, reduce process energy consumption.
Embodiment
Originally the cooperative processing method storing up EAF stainless steel slag and LF refining slag adopts following processing step: will store up EAF stainless steel slag, LF refining slag, coke powder and/or coal dust and be placed in respectively in loft drier be cooled to normal temperature after dry 3 ~ 6h at 100 ~ 120 DEG C; According to the percent mass proportioning of storing up EAF stainless steel slag 3% ~ 10%, LF refining slag 88% ~ 96%, coke powder and/or coal dust 1% ~ 2%, mixing of materials is evenly become to mix slag.Mix slag and load ceramic crucible, then ceramic crucible is put into microwave oven, with slag wool insulation around crucible, heat 30 ~ 90min under 150W ~ 900W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature.Cooled mixing slag adopts the method for conventional steel Slag treatment to carry out aftertreatment, can obtain innoxious, after process refining slag.
Below in conjunction with specific embodiment, the present invention is further detailed explanation, the material component in following embodiment and reaction process as described below.
(1) store up EAF stainless steel slag described in and derive from EAF explained hereafter stainless iron and steel enterprise stockyard, its main chemical compositions and content as shown in table 1.
Table 1: main chemical compositions and the content (quality %) of storing up EAF stainless steel slag
(2) main chemical compositions of described LF refining slag and content as shown in table 2.
The chemical composition of table 2:LF refining slag and content (quality %)
(3) carbon in described coke powder and fine coal can make to store up EAF stainless steel slag and store up the Cr that process oxidation generates 6+be reduced to Cr 3+, the principal reaction in microwave heating process is shown in that formula (1) is to formula (3):
2C+O 2→2CO(1)
3CO+2CrO 3→Cr 2O 3+3CO 2(2)
CO 2+C→2CO(3)。
Embodiment 1: gather and store up the EAF stainless steel slag of more than a year, this stores up the main chemical compositions of EAF stainless steel slag and content is: CaO40%, MgO8%, SiO 220%, Al 2o 35%, FeO8%, MnO2%, Cr 2o 32%, above-mentioned content is weight proportion.Gather cold conditions LF refining slag, the main chemical compositions of this LF refining slag and content are: CaO30%, MgO7%, SiO 26%, Al 2o 310%, FeO0.3%, Fe0.3%, above-mentioned content is weight proportion.Store up EAF stainless steel slag, LF refining slag and coke powder to be placed in respectively in loft drier to be cooled to normal temperature after dry 6h at 100 DEG C, according to storing up EAF stainless steel slag: LF refining slag: the mass ratio of coke powder=3:96:1, after mixing of materials is even, load ceramic crucible, then ceramic crucible is put into microwave oven, be incubated with slag wool around crucible, heat 90min under 150W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature, cooled mixing slag adopts the method for conventional steel Slag treatment to carry out aftertreatment, can obtain the refining slag after processing.Cr in refining slag after adopting GB5085.3-2007 to measure process 6+leaching concentration, result shows: Cr 6+leaching concentration < 5 μ g/L.
Embodiment 2: gather and store up the EAF stainless steel slag of more than a year, this stores up the main chemical compositions of EAF stainless steel slag and content is: CaO50%, MgO10%, SiO 230%, Al 2o 310%, FeO22%, MnO3%, Cr 2o 310%, above-mentioned content is weight proportion.Gather cold conditions LF refining slag, the main chemical compositions of this LF refining slag and content are: CaO70%, MgO16%, SiO 230%, Al 2o 345%, FeO2.5%, Fe2.5%, above-mentioned content is weight proportion.Store up EAF stainless steel slag, LF refining slag and coal dust to be placed in respectively in loft drier to be cooled to normal temperature after dry 5.5h at 105 DEG C, according to storing up EAF stainless steel slag: LF refining slag: the mass ratio of coal dust=5:94:1, after mixing of materials is even, load ceramic crucible, then ceramic crucible is put into microwave oven, be incubated with slag wool around crucible, heat 70min under 300W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature, the mixing slag of cooling adopts the method for conventional steel Slag treatment to carry out aftertreatment, can obtain the refining slag after processing.Cr in refining slag after adopting GB5085.3-2007 to measure process 6+leaching concentration, result shows: Cr 6+leaching concentration < 5 μ g/L.
Embodiment 3: gather and store up the EAF stainless steel slag of more than a year, this stores up the main chemical compositions of EAF stainless steel slag and content is: CaO45%, MgO9%, SiO 225%, Al 2o 37.5%, FeO15%, MnO2.5%, Cr 2o 36%, above-mentioned content is weight proportion.Gather cold conditions LF refining slag, the main chemical compositions of this LF refining slag and content are: CaO50%, MgO12%, SiO 218%, Al 2o 323%, FeO1.4%, Fe1.4%, above-mentioned content is weight proportion.Store up EAF stainless steel slag, LF refining slag and coke powder to be placed in respectively in loft drier to be cooled to normal temperature after dry 4.5h at 110 DEG C, according to storing up EAF stainless steel slag: LF refining slag: the mass ratio of coke powder=7:91:2, after mixing of materials is even, load ceramic crucible, then ceramic crucible is put into microwave oven, be incubated with slag wool around crucible, heat 50min under 450W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature, the mixing slag of cooling adopts the method for conventional steel Slag treatment to carry out aftertreatment, can obtain the refining slag after processing.Cr in refining slag after adopting GB5085.3-2007 to measure process 6+leaching concentration, result shows: Cr 6+leaching concentration < 5 μ g/L.
Embodiment 4: gather and store up the EAF stainless steel slag of more than a year, this stores up the main chemical compositions of EAF stainless steel slag and content is: CaO43%, MgO8.7%, SiO 227%, Al 2o 37.5%, FeO15.8%, MnO2.8%, Cr 2o 37.5%, above-mentioned content is weight proportion.Gather cold conditions LF refining slag, the main chemical compositions of this LF refining slag and content are: CaO46%, MgO11%, SiO 216%, Al 2o 321%, FeO0.9%, Fe0.8%, above-mentioned content is weight proportion.Store up EAF stainless steel slag, LF refining slag and coal dust to be placed in respectively in loft drier to be cooled to normal temperature after dry 3h at 115 DEG C, according to EAF stainless steel slag: LF refining slag: the mass ratio of coal dust=8:90:2, after mixing of materials is even, load ceramic crucible, then ceramic crucible is put into microwave oven, be incubated with slag wool around crucible, heat 40min under 900W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature, the mixing slag of cooling adopts the method for conventional steel Slag treatment to carry out aftertreatment, can obtain the refining slag after processing.Cr in refining slag after adopting GB5085.3-2007 to measure process 6+leaching concentration, result shows: Cr 6+leaching concentration < 5 μ g/L.
Embodiment 5: gather and store up the EAF stainless steel slag of more than a year, this stores up the main chemical compositions of EAF stainless steel slag and content is: CaO47%, MgO9.2%, SiO 223%, Al 2o 36.3%, FeO12.9%, MnO2.12%, Cr 2o 33.8%, above-mentioned content is weight proportion.Gather cold conditions LF refining slag, the main chemical compositions of this LF refining slag and content are: CaO54%, MgO13%, SiO 220%, Al 2o 325%, FeO1.5%, Fe1.6%, above-mentioned content is weight proportion.Store up EAF stainless steel slag, LF refining slag, coke powder and coal dust (weight ratio 1:1) are placed in respectively in loft drier and are cooled to normal temperature after dry 3.5h at 120 DEG C, according to EAF stainless steel slag: LF refining slag: the mass ratio of coke powder and coal dust=10:88:2, after mixing of materials is even, load ceramic crucible, then ceramic crucible is put into microwave oven, be incubated with slag wool around crucible, heat 30min under 600W microwave power after, close microwave oven, open fire door taking-up material and be cooled to normal temperature, the mixing slag of cooling adopts the method for conventional steel Slag treatment to carry out aftertreatment, the refining slag after processing can be obtained.Cr in refining slag after adopting GB5085.3-2007 to measure process 6+leaching concentration, result shows: Cr 6+leaching concentration < 5 μ g/L.

Claims (4)

1. store up the cooperative processing method of EAF stainless steel slag and LF refining slag for one kind, it is characterized in that: it will store up EAF stainless steel slag, LF refining slag, be mixed into coke powder and/or coal dust and mix slag, then mix slag after heating, cooling, aftertreatment, obtain the refining slag after processing.
2. the cooperative processing method storing up EAF stainless steel slag and LF refining slag according to claim 1, it is characterized in that, in described mixing slag, the mass percentage of each material is: store up EAF stainless steel slag 3% ~ 10%, LF refining slag 88% ~ 96%, coke powder and/or coal dust 1% ~ 2%.
3. the cooperative processing method storing up EAF stainless steel slag and LF refining slag according to claim 1 and 2, is characterized in that: adopt microwave to heat.
4. the cooperative processing method storing up EAF stainless steel slag and LF refining slag according to claim 3, is characterized in that: described microwave power is 150W ~ 900W, and heat-up time is 30 ~ 90min.
CN201510565156.9A 2015-09-08 2015-09-08 Store up the cooperative processing method of EAF stainless steel slags and LF refining slag Expired - Fee Related CN105200172B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510565156.9A CN105200172B (en) 2015-09-08 2015-09-08 Store up the cooperative processing method of EAF stainless steel slags and LF refining slag

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510565156.9A CN105200172B (en) 2015-09-08 2015-09-08 Store up the cooperative processing method of EAF stainless steel slags and LF refining slag

Publications (2)

Publication Number Publication Date
CN105200172A true CN105200172A (en) 2015-12-30
CN105200172B CN105200172B (en) 2017-08-25

Family

ID=54948126

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510565156.9A Expired - Fee Related CN105200172B (en) 2015-09-08 2015-09-08 Store up the cooperative processing method of EAF stainless steel slags and LF refining slag

Country Status (1)

Country Link
CN (1) CN105200172B (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002053351A (en) * 2000-08-07 2002-02-19 Sumitomo Metal Ind Ltd Pollution-free stainless steel slag and method for manufacturing the same
CN1528532A (en) * 2003-10-10 2004-09-15 匡少平 Method for harmless treating chromium slag into resource and use thereof
CN101138670A (en) * 2006-09-08 2008-03-12 隋智通 Novel process of the high temperature reduction and detoxication of industrial chromic slag
CN101264481A (en) * 2008-04-30 2008-09-17 钢铁研究总院 Cr6+ furnace cinder containing gas reduction curing method
CN101549894A (en) * 2009-05-21 2009-10-07 昆明理工大学 Method of using lake sediment in microwave detoxification of chromium slags
CN101569783A (en) * 2009-06-08 2009-11-04 昆明理工大学 Method for detoxicating chromium residue by utilizing high sulfur petroleum coke through microwave
CN101569784A (en) * 2009-06-08 2009-11-04 昆明理工大学 Method for detoxicating chromium residue by utilizing coal refuse through microwave
CN101942571A (en) * 2010-09-06 2011-01-12 重庆瑞帆再生资源开发有限公司 Method for innocently treating and recycling chromium residues and metallurgical waste material
CN103638629A (en) * 2013-12-10 2014-03-19 西南科技大学 Process for integrally reducing solidified chromium slag

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002053351A (en) * 2000-08-07 2002-02-19 Sumitomo Metal Ind Ltd Pollution-free stainless steel slag and method for manufacturing the same
CN1528532A (en) * 2003-10-10 2004-09-15 匡少平 Method for harmless treating chromium slag into resource and use thereof
CN101138670A (en) * 2006-09-08 2008-03-12 隋智通 Novel process of the high temperature reduction and detoxication of industrial chromic slag
CN101264481A (en) * 2008-04-30 2008-09-17 钢铁研究总院 Cr6+ furnace cinder containing gas reduction curing method
CN101549894A (en) * 2009-05-21 2009-10-07 昆明理工大学 Method of using lake sediment in microwave detoxification of chromium slags
CN101569783A (en) * 2009-06-08 2009-11-04 昆明理工大学 Method for detoxicating chromium residue by utilizing high sulfur petroleum coke through microwave
CN101569784A (en) * 2009-06-08 2009-11-04 昆明理工大学 Method for detoxicating chromium residue by utilizing coal refuse through microwave
CN101942571A (en) * 2010-09-06 2011-01-12 重庆瑞帆再生资源开发有限公司 Method for innocently treating and recycling chromium residues and metallurgical waste material
CN103638629A (en) * 2013-12-10 2014-03-19 西南科技大学 Process for integrally reducing solidified chromium slag

Also Published As

Publication number Publication date
CN105200172B (en) 2017-08-25

Similar Documents

Publication Publication Date Title
CN101717842B (en) Method for dephosphorization and desulphurization in process of steel production in induction furnace
CN109022644B (en) Method for recovering slag desulfurization and dephosphorization in cooperation with ferrite in full-three-removal process
CN101721784B (en) Harm-free and recycling treatment method for chromium slag
CN102796879B (en) Method for preparing chromium-containing iron powder by direct reduction of calcium-free chromium slag
Drissen et al. Recent development in slag treatment and dust recycling
CN102719574A (en) Converter steel slag stability modifier and use method thereof
CN107287367A (en) Method for recovering iron by utilizing high-iron red mud
CN105039615B (en) Store up the processing method of AOD stainless steel slags
CN102719575B (en) Converter steel slag modifier and manufacturing and using methods thereof
CN103993134A (en) Steelmaking slag melting agent and use method thereof
CN105506226A (en) Method for carrying out pre-desiliconization, pre-decarburization and pre-dephosphorization on molten iron in molten iron tank
CN103031401B (en) Method for converter steelmaking by LF (Ladle Furnace) refining furnace reducing slag
CN115679097A (en) Method for recycling iron-making gas ash by using converter slag and refined dedusting ash
CN101403023A (en) Ultra-deep desulfuration method for hot metal
CN106755657A (en) A kind of method that titaniferous mixing slag metallurgy melting reduction is reclaimed
CN105039616A (en) Coprocessing method for AOD stainless steel residues stored in piles and LF refining residues
CN114150109B (en) Process for harmlessly converting desiliconized dephosphorized slag of converter and secondary aluminum ash in cooperation with chromium slag
CN100387732C (en) Harmless resource utilization method for chromic slag
CN102864271A (en) Digestion process of vanadium extraction waste slag in semi-steel steelmaking converter
CN104651553A (en) Steel slag modifier
CN102776310B (en) Pretreating dephosphorizing agent for molten iron containing metallic magnesium residues
CN105200172B (en) Store up the cooperative processing method of EAF stainless steel slags and LF refining slag
Cao et al. Selective stabilization of chromium and sustainable treatment of stainless steel slags
CN101760609A (en) Iron ore composite pellet and production method thereof
Gao et al. Fundamental research in comprehensive utilization of Bayan Obo ore by direct reduction

Legal Events

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

Granted publication date: 20170825

Termination date: 20200908