CN108913878A - A kind of arsenic removing method of iron ore - Google Patents
A kind of arsenic removing method of iron ore Download PDFInfo
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- CN108913878A CN108913878A CN201810890071.1A CN201810890071A CN108913878A CN 108913878 A CN108913878 A CN 108913878A CN 201810890071 A CN201810890071 A CN 201810890071A CN 108913878 A CN108913878 A CN 108913878A
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- 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
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/11—Removing sulfur, phosphorus or arsenic other than by roasting
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- 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
- C22B1/00—Preliminary treatment of ores or scrap
- C22B1/02—Roasting processes
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
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Abstract
The invention discloses a kind of arsenic removing methods of iron ore, include the following steps:1)Prepare ore pulp;2)Biological dearsenification;3)Grinding;4)Oxidizing roasting, specially by step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, the carrier gas and constantly stirred mixture C during oxidizing roasting, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification iron ore after oxidizing roasting;5)Recycling circulation.The present invention effectively increases dearsenification efficiency by the mutual cooperation of biological dearsenification and gasification dearsenification to the dearsenification significant effect of the stone containing symplesite;Meanwhile the gasification dearsenification product of generation reduces by recycling and recycling processing and causes environmental pollution to environment, environmental pollution is small, is advantageously implemented the comprehensive utilization of the mineral resources containing arsenic.
Description
Technical field
The present invention relates to ore processing technical field, the arsenic removing method of specifically a kind of iron ore.
Background technique
Iron ore is produced in steel and is looked forward to as containing iron simple substance or iron compound and the mineral aggregate of economic utilization is capable of
It is highly important raw material in industry.There are many impurity in iron ore, according to it to smelting process and its to the shadow of product quality
Ringing can be divided into beneficial with harmful two class again, and common and most important objectionable impurities has sulphur, phosphorus, arsenic, potassium, sodium, fluorine etc..Its
In, arsenic can largely enter the pig iron when smelting as the harmful element in iron ore, generate to steel performance a series of bad
It influences, such as steel heat machined surface can be caused to be cracked, reduce the impact flexibility of steel, increase the brittleness of steel, and then reduce the matter of steel
Amount, influences the welding performance of steel.
Currently, existing arsenic removing method is mostly the dearsenicating technology that gasifies, although can remove in iron ore to a certain extent
Arsenic, but arsenic-removing rate is low, and the gasification dearsenification product of generation is mostly extremely toxic substance, be easy to cause environmental pollution, brings serious
Environmental problem.Therefore, the arsenic removing method for designing a kind of iron ore that environmental pollution is small, for reducing arsenic in smelting system
Harm, realize the mineral resources containing arsenic comprehensive utilization be of great significance to.
Summary of the invention
The purpose of the present invention is to provide a kind of arsenic removing methods of iron ore, to solve mentioned above in the background art ask
Topic.
To achieve the above object, the present invention provides the following technical solutions:
A kind of arsenic removing method of iron ore, which is characterized in that it includes the following steps:
1)Prepare ore pulp:It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials
The 88-98% of total weight of material is accounted for for the part of 20-40 mesh, and suitable deionized water is then added and carries out mechanical stirring mixing
It is even, then ultrasonic disperse processing 20-40min is carried out, obtain the ore pulp A that concentration is 6-18%;It is handled by ultrasonic disperse, is effectively mentioned
The high dispersion effect of material;
2)Biological dearsenification:By step 1)Obtained in the strain mixed liquor of 0.1-0.2 times of weight is added in ore pulp A, then use concentration
It is 3 for 98% sulphur acid for adjusting pH value, stands 8-16 days at 18-36 DEG C, be filtered to remove liquid, it is dry, obtain mixture B;
3)Grinding:By step 2)Obtained in the coke of 0.3-0.7 times of weight is added in mixture B, ground and mixed is uniform, obtains mixed
Close material C;
4)Oxidizing roasting:By step 3)Obtained in mixture C carry out oxidizing roasting under weak oxide atmosphere, and roasted in oxidation
The carrier gas constantly stirred mixture C during burning, and be passed through flowing is used to drive the gas D of generation, and gained is solid after oxidizing roasting
Body is dearsenification iron ore;
5)Recycling circulation:By step 4)The gas D of middle generation gathers dust under the conditions of 450-750 DEG C of temperature, and what is obtained is heavy
Object return step 1 drops)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that remaining gas
Arsenic oxide arsenoxide in body is condensed into solid and gather dust.
As a further solution of the present invention:Step 1)In, the supersonic frequency of the ultrasonic disperse is 20-40kHz.
As further scheme of the invention:Step 1)In, the churned mechanically stirring rate is 500-900r/
min。
As further scheme of the invention:Step 2)In, the strain mixed liquor is cultivated in sanitary sewage
Reach the acidithiobacillus ferrooxidans, Siberia Sulfobacillus and ferrous oxide hook end spirillum of logarithmic growth phase according to body
Product is than being 3:1:2 ratio mixes.
As further scheme of the invention:Step 4)In, the temperature of the oxidizing roasting is 750-950 DEG C;It is described
The calcining time of oxidizing roasting is 20-5Omin.
As further scheme of the invention:Step 4)In, the CO in the weak oxide atmosphere2/ CO volume ratio is 2:
1。
As further scheme of the invention:Step 5)In, the carrier gas is that vapor and air are according to volume ratio
5:1 ratio mixes;The flow velocity of the carrier gas is 0.3-0.7m/s.
Application of the arsenic removing method of the iron ore in preparation dearsenification iron ore product.
Compared with prior art, the beneficial effects of the invention are as follows:
The present invention effectively proposes the dearsenification significant effect of the stone containing symplesite by the mutual cooperation of biological dearsenification and gasification dearsenification
High dearsenification efficiency;Meanwhile the gasification dearsenification product of generation reduces by recycling and recycling processing and causes environment to environment
Pollution, environmental pollution is small, is advantageously implemented the comprehensive utilization of the mineral resources containing arsenic.
Specific embodiment
Technical solution of the present invention is described in more detail With reference to embodiment.
Embodiment 1
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 20min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 12 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 850 DEG C;The calcining time of the oxidizing roasting is 35min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 2
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 40min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 12 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 850 DEG C;The calcining time of the oxidizing roasting is 35min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 3
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 30min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 12 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 850 DEG C;The calcining time of the oxidizing roasting is 35min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 4
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 30min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 8 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 850 DEG C;The calcining time of the oxidizing roasting is 35min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 5
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 30min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 16 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 850 DEG C;The calcining time of the oxidizing roasting is 35min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 6
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 30min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 12 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 750 DEG C;The calcining time of the oxidizing roasting is 20min;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
Embodiment 7
A kind of arsenic removing method of iron ore, it includes the following steps:
1)It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials is the portion of 30 mesh
Divide and account for the 93% of total weight of material, it is mixed with the stirring rate progress mechanical stirring of 700r/min that suitable deionized water is then added
It closes uniformly, then ultrasonic disperse is carried out with the supersonic frequency of 30kHz and handles 30min, obtain the ore pulp A that concentration is 12%;Pass through ultrasound
Decentralized processing effectively increases the dispersion effect of material;
2)By step 1)Obtained in be added the strain mixed liquor of 0.15 times of weight in ore pulp A, then with concentration for 98% sulfuric acid tune
Saving pH value is 3, stands 12 days at 27 DEG C, is filtered to remove liquid, dry, obtains mixture B;
Wherein, the strain mixed liquor is the ferrous oxide acidophilus sulphur bar for reaching logarithmic growth phase cultivated in sanitary sewage
Bacterium, Siberia Sulfobacillus and ferrous oxide hook end spirillum are 3 according to volume ratio:1:2 ratio mixes.
3)By step 2)Obtained in the coke of 0.5 times of weight is added in mixture B, ground and mixed is uniform, obtains mixture
C;
4)By step 3)Obtained in mixture C oxidizing roasting is carried out under weak oxide atmosphere, and during oxidizing roasting
The carrier gas constantly stirred mixture C, and be passed through flowing is used to drive the gas D of generation, and obtained solid is dearsenification after oxidizing roasting
Iron ore;
Wherein, the temperature of the oxidizing roasting is 950 DEG C;The calcining time of the oxidizing roasting is 5Omin;The weak oxide gas
CO in atmosphere2/ CO volume ratio is 2:1.
5)By step 4)The gas D of middle generation gathers dust under the conditions of 600 DEG C of temperature, and obtained sediment returns to step
Rapid 1)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that the oxidation in residual gas
Arsenic is condensed into solid and gather dust;Wherein, it according to volume ratio is 5 that the carrier gas, which is vapor and air,:1
Ratio mixes;The flow velocity of the carrier gas is 0.5m/s.
The present invention has the dearsenification significant effect of the stone containing symplesite by the mutual cooperation of biological dearsenification and gasification dearsenification
Effect improves dearsenification efficiency;Meanwhile the gasification dearsenification product of generation is reduced and is caused to environment by recycling and recycling processing
Environmental pollution, environmental pollution is small, is advantageously implemented the comprehensive utilization of the mineral resources containing arsenic.
Better embodiment of the invention is explained in detail above, but the present invention is not limited to above-mentioned embodiment party
Formula within the knowledge of one of ordinary skill in the art can also be without departing from the purpose of the present invention
Various changes can be made.
Claims (10)
1. a kind of arsenic removing method of iron ore, which is characterized in that it includes the following steps:
1)Prepare ore pulp:It symplesite stone will be contained will put into ball mill and carry out grinding, grinding granularity into obtained ore materials
The 88-98% of total weight of material is accounted for for the part of 20-40 mesh, and suitable deionized water is then added and carries out mechanical stirring mixing
It is even, then ultrasonic disperse processing 20-40min is carried out, obtain the ore pulp A that concentration is 6-18%;
2)Biological dearsenification:By step 1)Obtained in the strain mixed liquor of 0.1-0.2 times of weight is added in ore pulp A, then use concentration
It is 3 for 98% sulphur acid for adjusting pH value, stands 8-16 days at 18-36 DEG C, be filtered to remove liquid, it is dry, obtain mixture B;
3)Grinding:By step 2)Obtained in the coke of 0.3-0.7 times of weight is added in mixture B, ground and mixed is uniform, obtains mixed
Close material C;
4)Oxidizing roasting:By step 3)Obtained in mixture C carry out oxidizing roasting under weak oxide atmosphere, and roasted in oxidation
The carrier gas constantly stirred mixture C during burning, and be passed through flowing is used to drive the gas D of generation, and gained is solid after oxidizing roasting
Body is dearsenification iron ore;
5)Recycling circulation:By step 4)The gas D of middle generation gathers dust under the conditions of 450-750 DEG C of temperature, and what is obtained is heavy
Object return step 1 drops)It is middle to be used as stone containing symplesite, residual gas is finally subjected to waste heat recovery processing, so that remaining gas
Arsenic oxide arsenoxide in body is condensed into solid and gather dust.
2. the arsenic removing method of iron ore according to claim 1, which is characterized in that step 1)In, the ultrasonic disperse
Supersonic frequency is 20-40kHz.
3. the arsenic removing method of iron ore according to claim 2, which is characterized in that step 1)In, it is described churned mechanically
Stirring rate is 500-900r/min.
4. the arsenic removing method of iron ore according to claim 1, which is characterized in that step 2)In, the strain mixed liquor
For the acidithiobacillus ferrooxidans for reaching logarithmic growth phase, Siberia Sulfobacillus and oxidation cultivated in sanitary sewage
Ferrous hook end spirillum is 3 according to volume ratio:1:2 ratio mixes.
5. the arsenic removing method of iron ore according to claim 1, which is characterized in that step 4)In, the oxidizing roasting
Temperature is 750-950 DEG C.
6. the arsenic removing method of iron ore according to claim 5, which is characterized in that step 4)In, the oxidizing roasting
Calcining time is 20-5Omin.
7. the arsenic removing method of iron ore according to claim 6, which is characterized in that step 4)In, the weak oxide atmosphere
In CO2/ CO volume ratio is 2:1.
8. the arsenic removing method of iron ore according to claim 1, which is characterized in that step 5)In, the carrier gas is water steaming
Gas and air are 5 according to volume ratio:1 ratio mixes.
9. the arsenic removing method of iron ore according to claim 8, which is characterized in that step 5)In, the flow velocity of the carrier gas
For 0.3-0.7m/s.
10. a kind of arsenic removing method of the iron ore as described in claim 1-9 is any answering in preparation dearsenification iron ore product
With.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113293299A (en) * | 2021-05-07 | 2021-08-24 | 云南省生态环境科学研究院 | Resource utilization method for arsenic-containing hazardous waste |
CN115011804A (en) * | 2021-12-23 | 2022-09-06 | 昆明理工大学 | Method for removing arsenic by co-roasting high-arsenic antimony-lead anode mud air and water vapor |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102251099A (en) * | 2011-07-14 | 2011-11-23 | 北京科技大学 | Method for removing arsenic, sulfur and phosphorus by using thiobacillusacidophilus |
CN103820587A (en) * | 2013-12-11 | 2014-05-28 | 昆明理工大学 | Method for removing arsenic from arsenic-containing iron-rich slag by volatilization |
-
2018
- 2018-08-07 CN CN201810890071.1A patent/CN108913878A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102251099A (en) * | 2011-07-14 | 2011-11-23 | 北京科技大学 | Method for removing arsenic, sulfur and phosphorus by using thiobacillusacidophilus |
CN103820587A (en) * | 2013-12-11 | 2014-05-28 | 昆明理工大学 | Method for removing arsenic from arsenic-containing iron-rich slag by volatilization |
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