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Method for synchronously leaching and separating antimony, arsenic and alkali in arsenic alkali residue

An arsenic-alkali slag and leaching technology, which is applied in the field of comprehensive utilization of environmental protection and waste resources, can solve the problems of poor economy, high pollution hidden dangers, and high energy consumption for processing, and achieves good separation effect, no secondary pollution, and large processing capacity Effect

Active Publication Date: 2019-09-03
长沙紫宸科技开发有限公司
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0017] The above-mentioned fire treatment method requires harsh conditions for thermal reduction treatment, requiring a closed vacuum electric arc furnace, vacuuming with a vacuum pump, and forced vacuuming under high temperature conditions for 1 to 8 hours. The control requirements for this intermittent fire reduction treatment are very strict. , has high requirements for equipment and operation control, and may only be suitable for laboratory or small-batch metallurgical treatment, and the adaptability of large-scale industrial production is doubtful; it is also not suitable for processing arsenic-alkali slag containing a large amount of antimony, which uses a vacuum pump to continuously Under the condition of strong vacuuming at ≥800°C, the volatilization of antimony vapor will occur simultaneously with the sublimation of arsenic (arsenic sublimates at 615°C), and often only arsenic-antimony alloys are obtained; and it is difficult to deal with arsenic acid containing antimonate in large quantities Salt, using carbon as a reducing agent to smelt arsenic-alkali slag, the overall reducing ability is still extremely weak when the reducing temperature is lower than 800°C, and the reducing ability will be better when the temperature is above 900°C, and the higher the treatment temperature for hazardous waste, the less It’s just a problem of high energy consumption and higher equipment requirements, and the potential risk of accidents is even greater, and because the closed reduction furnace is used to rest the carbon powder to reduce the vacuum process, the crude antimony and lead still contains arsenic, and the reduction slag still contains arsenic. Not a small amount of arsenic (including soluble arsenate and insoluble arsenate) still only achieves the purpose of partial reduction and separation. Whether it is the return of crude antimony to refining or the return of reducing slag as arsenic removal agent, it has caused the cycle of arsenic
Even under strict control of the reaction conditions, the water leached slag separated from the reduced slag after water leaching still contains a certain amount of arsenic, which is still a hazardous solid waste that needs to be treated; the arsenic vapor or arsenic flue gas or elemental arsenic It is easy to be oxidized, especially in the process of forcibly pumping out from the high-temperature furnace with a vacuum pump to cooling. Even if a mixed atmosphere of inert gas and / or nitrogen and hydrogen and / or carbon monoxide is used, it is extremely difficult to recycle and reuse, which will easily lead to economical pollution. Poor performance or air pollution, and the vacuum pump relied on for vacuuming arsenic flue gas has extremely poor adaptability to metal particles or flue gas dust, making it difficult to ensure normal production and operation; or it is necessary to strictly control the equivalent ratio of sodium and phosphate The reaction conditions for the generation of trisodium phosphate are to simultaneously reduce the antimonate and arsenate in the arsenic-alkali slag to elemental antimony and elemental arsenic, but the production control habits of actual antimony smelting enterprises are difficult to guarantee the seemingly simple reaction conditions , and its processing energy consumption is high, and the potential pollution hazard is large, especially the arsenic-containing trisodium phosphate scum can easily flow into the agricultural fertilizer market quietly, resulting in uncontrollable spread of pollution
[0018] In summary, the separation of arsenic, antimony, and alkali in the existing treatment processes for various types of arsenic-alkali slag is relatively difficult, and problems such as environmental protection and economy are prominent.
The current domestic wet process is all focused on hot water leaching or oxidative water leaching, but there is no report on the research or practice of separating arsenic-alkali slag by leaching with aqueous glycerin

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0045] As 9.73%, Sb 26.18%, Pb 5.79%, and Na 22.76% were detected by using arsenic-alkali slag from an antimony smelter; commercially available industrial glycerin (content 98.5%), caustic soda (caustic soda NaOH content 96%), hydrochloric acid ( content 35%), phytic acid (content 95%), liquefied carbon dioxide as raw materials, and tap water as water.

[0046] This embodiment includes the following steps: grind to 200 mesh sieve remaining 3% of the arsenic-alkali slag powder into the soaking tank, according to the mass ratio of arsenic-alkali slag powder: water: glycerin: caustic soda = 1:3:2:0.73 Add water, glycerin, and caustic soda, control the pH value to be stable at 14, stir and soak for 3 hours at normal pressure and 85°C, and separate to obtain silicon-aluminum mineral slag, alkali-glycerin aqueous solution (containing glycerol complex, caustic soda, arsenate and soda ash mixed solution); alkali glycerin aqueous solution cooled to 0 ° C to crystallize and separate to ...

Embodiment 2

[0050] The arsenic-alkali slag from an antimony smelter was selected, and As 11.26%, Sb 24.35%, Pb 2.77%, and Na 24.12% were detected; commercially available industrial glycerin (content 98.5%), caustic soda (caustic soda NaOH content 96%), hydrochloric acid ( content 35%), phytic acid (content 95%), liquefied carbon dioxide as raw materials, and tap water as water.

[0051] The present embodiment comprises the following steps: setting the leaching mass ratio of arsenic-alkali slag to be arsenic-alkali slag: water: glycerin: caustic soda=1:3.5: 2.5: 0.95, first arsenic-alkali slag and water, glycerin by mass ratio 1 Grind together at a ratio of 2:1 to form a slurry with a particle size of <74 μm, send it into the soaking tank, make up the amount of water, glycerin, and caustic soda, control the pH value to stabilize at 14, stir and soak at normal pressure and 95°C After 1.5 hours, separate to obtain silicon-aluminum mineral slag and aqueous alkali glycerin solution; cool the a...

Embodiment 3

[0055] The arsenic-alkali slag from a certain antimony smelter was selected, and As 17.84%, Sb 14.87%, Pb 3.42%, Na 26.70% were detected; commercially available industrial glycerin (content 98.5%), caustic soda (caustic soda NaOH content 96%), hydrochloric acid ( content 35%), phytic acid (content 95%), liquefied carbon dioxide as raw materials, and tap water as water.

[0056] The present embodiment comprises the following steps: setting the soaking mass ratio of arsenic-alkali slag to be arsenic-alkali slag: water: glycerol: caustic soda=1:4: 2.5: 1.3, and first arsenic-alkali slag and water, glycerin by mass ratio 1 Grind together at a ratio of 2:1 to form a slurry with a particle size of <74 μm, send it into the soaking tank, make up the amount of water, glycerin, and caustic soda, control the pH value to stabilize at 14, stir and soak at normal pressure and 90°C After 1.2 hours, separate to obtain silicon-aluminum mineral slag and aqueous alkali glycerin solution; cool th...

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Abstract

The invention discloses a method for synchronously leaching and separating antimony, arsenic and alkali in arsenic alkali residue. The method comprises the following steps of putting a mixture of water, glycerol and caustic soda with the crushed and ground arsenic alkali residue added or putting ground slurry of the arsenic alkali residue, the water, the glycerol and the caustic soda into a leaching tank, controlling the pH value, carrying out leaching extraction and solid-liquid separation to obtain silicon-aluminum ore slag and an alkali-glycerol aqueous solution; carrying out the dearsenification, deleading, antimony removal and purification and precipitation treatment in the obtained alkali glycerin aqueous solution sequentially to obtain arsenate crystals, lead slag, antimony oxide, aphytate precipitate and a glycerol sodium carbonate aqueous solution; carrying out nanofiltration or reverse osmosis membrane chromatography in the glycerol sodium carbonate aqueous solution to obtain a nanofiltration concentrated solution and a dialysate glycerol aqueous solution; returning the obtained dialysate glycerol aqueous solution to the leached arsenic alkali residue; carrying out spraydrying on the obtained nanofiltration concentrated solution to prepare sodium carbonate or caustic soda by adding lime in causticizing method; and using the obtained antimony oxide for returning antimony refining or processing antimony or refining antimony oxide and antimonate. According to the method, the antimony, arsenic and alkali in the arsenic alkali residue can be synchronously leached andseparated, and the solvent can be recycled.

Description

technical field [0001] The invention relates to the technical field of comprehensive utilization of environmental protection waste resources, in particular to a resource utilization method for synchronous leaching and separation of antimony, arsenic and alkali in arsenic-alkali slag. Background technique [0002] Arsenic-alkali slag is a kind of arsenic-containing sodium arsenate, sodium antimonate, sodium carbonate and a certain amount of aluminosilicate minerals and compounds such as lead and bismuth produced during the antimony refining and arsenic removal process of antimony by fire method. Smelting waste residue, because sodium arsenate and sodium arsenite is highly toxic and easily soluble in water, can easily lead to environmental pollution incidents. It has been difficult to properly handle solid hazardous waste, which has restricted the healthy development of the antimony smelting industry to a certain extent. [0003] For the arsenic-alkali slag that is difficult t...

Claims

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Application Information

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IPC IPC(8): C22B7/00C22B1/11C22B30/02C22B30/04C22B30/06C22B13/00C01D7/07
CPCC01D7/07C22B1/11C22B7/008C22B13/045C22B30/02C22B30/04C22B30/06Y02P10/20
Inventor 尹小林
Owner 长沙紫宸科技开发有限公司