CN109881015A - A kind of method of arsenic sulfide slag processing co-production elemental arsenic - Google Patents

A kind of method of arsenic sulfide slag processing co-production elemental arsenic Download PDF

Info

Publication number
CN109881015A
CN109881015A CN201910320272.2A CN201910320272A CN109881015A CN 109881015 A CN109881015 A CN 109881015A CN 201910320272 A CN201910320272 A CN 201910320272A CN 109881015 A CN109881015 A CN 109881015A
Authority
CN
China
Prior art keywords
arsenic
sulfide slag
silicon
elemental
vacuum distillation
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
CN201910320272.2A
Other languages
Chinese (zh)
Other versions
CN109881015B (en
Inventor
丘克强
丁杰
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.)
Central South University
Original Assignee
Central South University
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 Central South University filed Critical Central South University
Priority to CN201910320272.2A priority Critical patent/CN109881015B/en
Publication of CN109881015A publication Critical patent/CN109881015A/en
Application granted granted Critical
Publication of CN109881015B publication Critical patent/CN109881015B/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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Silicon Compounds (AREA)

Abstract

The invention belongs to harmful field of solid waste disposal; a kind of method for specifically disclosing arsenic sulfide slag processing co-production elemental arsenic; by arsenic sulfide slag, silicon mixture protective atmosphere, not less than 550 at a temperature of react, by reaction product through vacuum distillation, the elemental arsenic is made;The granularity of the silicon is less than or equal to 300 mesh;Reaction time is not less than 90min.Present invention research has been surprisingly found that, displacement reaction is carried out under the conditions of the temperature by arsenic sulfide slag, elementary silicon, cooperation is to silicon grain diameter, reaction time and subsequent vacuum distillation, the yield and purity of elemental arsenic can be unexpectedly obviously improved, silicon disulfide obtained can be used as the raw material of production hydrogen sulfide gas simultaneously, and hydrogen sulfide gas can handle industrial " waste acid " waste water as vulcanizing agent again.

Description

A kind of method of arsenic sulfide slag processing co-production elemental arsenic
Technical field
The present invention relates to arsenide processing to utilize field, and in particular to a kind of reacting from arsenones using arsenones and silicon The method of elemental arsenic is recycled in slag.
Background technique
Arsenic is resource indispensable in the national economic development, is had in fields such as agricultural, electronics, medicine, metallurgy, chemical industry Special purposes.It often is applied to Insecticides (tech) & Herbicides (tech) and timber preservative, decolorising agent, non-ferrous alloy, ceramics etc., especially Its in a semiconductor material using more and more.Arsenic is widely present among various ores, Chang Yuqian, copper, zinc, tin, tungsten, The metalliferous minerals association such as antimony, gold, in the processing smelting process of these ores, significant component of arsenic enters diluted acid waste water In.Currently, the processing of this diluted acid waste water mostly uses greatly vulcanization, to generate a large amount of arsenic sulfide slag.Due to these vulcanizations Arsenic Slag treatment disposition difficulty is larger, and many smelteries all take the modes such as directly stacking, stabilisation landfill to dispose.And arsenones contain There is severe toxicity, such disposal options, which exist, generates the hidden danger seriously endangered to soil environment and human health.Therefore, from sulphur Change recycling arsenic resource in arsenic slag to be not only environmental protection, the needs of human health and resource and make full use of, national economy is lasting The needs of development.
It is directed to arsenic sulfide slag at present, main treatment process has pyrogenic process and wet process two major classes.Arsenic sulfide slag passes through in pyrogenic process Oxidizing roasting, arsenones therein are converted to arsenic trioxide and are directly volatized into flue gas, and then arsenic trioxide is realized in condensation Recycling.The shortcomings that this method is poor product quality, and the sulfur dioxide flue gas of association is high containing arsenic, it is difficult to handle, secondary pollution is serious. Wet process mainly takes acidleach, alkali leaching or salt to be impregnated into capable processing, and first arsenic is separated from slag, and then further recycling arsenic produces Product carry out harmless treatment.But the universal production procedure of wet-treating is complicated, processing cost is higher.
Patent CN106756113A discloses a kind of method that arsenic sulfide slag reduction sulphur fixing roast directly produces metallic arsenic, with Arsenic sulfide slag is raw material, and copper oxide and reducing agent is added, and restores sulphur fixing roast after mixing at high temperature, product of roasting is through vacuum point From obtaining elemental arsenic.Although the method process is simple, used oxidation copper processing is more expensive, obtains unit mass elemental arsenic product Consumption oxidation copper mass is larger, and obtained elemental arsenic purity is not high, and the rate of recovery is lower.In addition to this, which is using raw material Untreated arsenic sulfide slag does not only result in copper oxide and contacts poor, target with arsenones containing a large amount of other metal sulfides Reaction efficiency is low, while increasing energy consumption, reduces equipment service efficiency.
Patent CN103922294A discloses a kind of method that arsenic is recycled from arsenic sulfide slag, using arsenic sulfide slag as raw material, The very high arsenones of purity are obtained with the method processing arsenic sulfide slag of staged vacuum distillation first, it is then mixed with iron powder and arsenones Conjunction is reacted at high temperature, and reaction product obtains elemental arsenic through vacuum separation.The method process is simple, the purified processing of arsenic sulfide slag Afterwards, it can better contact with and react with iron powder.But side reaction easily occurs with iron and generates arsenic iron compound, drop for the elemental arsenic that the method generates Also the rate of recovery of arsenic is seriously reduced while the utilization rate of low iron powder.
Summary of the invention
For the limitation of the processing method of existing arsenic sulfide slag, the object of the present invention is to provide a kind of simplicity, cost It is cheap, the rate of recovery is high, in the slave arsenic sulfide slag of safety and environmental protection recycle elemental arsenic method.
A kind of method of arsenic sulfide slag processing co-production elemental arsenic, by arsenic sulfide slag, silicon mixture in protective atmosphere, no Reaction (displacement reaction), by reaction product through vacuum distillation, is made the elemental arsenic at a temperature of lower than 550;
The granularity of the silicon is less than or equal to 300 mesh;
Reaction time is not less than 90min.
Present invention research has been surprisingly found that, carries out displacement reaction under the conditions of the temperature by arsenic sulfide slag, elementary silicon, Cooperation to silicon grain diameter, reaction time and subsequent vacuum distillation, can unexpectedly be obviously improved elemental arsenic yield and Purity, while silicon disulfide obtained can be used as the raw material of production hydrogen sulfide gas, hydrogen sulfide gas can be used as vulcanizing agent again Handle industrial " waste acid " waste water.
Preferably, the arsenic sulfide slag is before mixing in advance through vacuum distillation purification processes.The study found that its into Row vacuum distillation purification processes, the more conducively preparation of elemental arsenic.
Preferably, the temperature of vacuum distillation purification processes process is 400-600 DEG C, pressure 10-400Pa.
Preferably, the vacuum distillation purification processes time is not less than 1h.
In the present invention, the granularity of the silicon is less than or equal to 300 mesh;Preferably 300~1250 mesh.Present invention research hair It is existing, under the preparating mechanism that the present invention innovates, using small silicon, facilitate the purity for unexpectedly promoting elemental arsenic obtained And the rate of recovery.
Preferably, the silicon is not less than the theoretical molar amount for reacting the arsenones in arsenic sulfide slag completely.
Preferably, the silicon is 1~2 times of the theoretical molar amount for reacting the arsenones in arsenic sulfide slag completely.
In the present invention, to be further conducive to arsenic sulfide slag being converted to elemental arsenic, need to control the temperature at 550 DEG C Or more.
Preferably, reaction temperature is 550-600 DEG C.
Reaction process preferably carries out under protective atmosphere, and the protective atmosphere is, for example, nitrogen or inert gas.
Preferably, the reaction time is 90-120min.
In the present invention, it is preferred to use the method for vacuum distillation recycles elemental arsenic from the reaction product.
Preferably, the pressure of vacuum distillation process is 15-25Pa;Temperature is 500-600 DEG C.
Preferably, the vacuum distillation time is not less than 60min;Further preferably 60-90min.
The present invention is a kind of to extract the method that pure arsenones and pasc reaction prepare elemental arsenic from arsenic sulfide slag, it includes following Step:
(1) by arsenones and excessive silicon powder mixed grinding, in inert gas atmosphere, normal pressure reacts at 550-600 DEG C; Reaction time is preferably 90-120min.
(2) by reaction product obtained in (1) step in pressure 15-25Pa, temperature is steamed under conditions of being 500-600 DEG C It evaporates, obtains the condensate of elemental arsenic;Distillation time is preferably 60-90min.
Under reaction temperature of the invention, the present invention prepares elemental arsenic process, the reaction mainly occurred such as following formula (1), As2S3+ 3/2Si=2As+3/2SiS2 (1)
Arsenic sulfide slag is handled using the mechanism that the present invention innovates, can efficiently realize the arsenic conversion of arsenic sulfide slag, and is not easy By-product is generated, the rate of recovery of arsenic is higher.
Beneficial effects of the present invention
The method of the present invention, for the purity of elemental arsenic obtained up to 99% or more, the rate of recovery of arsenic reaches 95% or more.We Method process flow is short, and operating condition is easy to control, whole process safety and environmental protection, and the metallic arsenic product of acquisition can directly carry out industry and answer With or further Refining is high purity arsenic for semi-conductor industry.And the raw material silicon powder for being used for reduction-sulfurization arsenic is high-efficient, It is cheap, greatly reduce the cost of arsenic recycling.In general, the present invention is preferably realized by arsenones to elemental arsenic Transformation, and then be arsenones waste residue resource using a new technical solution is provided, substantially reduce stockpiling hazard waste, tool There are significant economic benefit and environmental benefit, is worthy of popularization.
Detailed description of the invention
Fig. 1 is EDS (Method of Energy-Dispersive X-Ray Fluorescence Spectrometer instrument) detection for the steaming thing that the embodiment of the present invention 1 obtains Result figure.
As can be seen from the figure resulting elemental arsenic mass percent reaches 99.51%.
Specific embodiment
The main component of the arsenic sulfide slag (dry slag) of this experiment is (wt.%): As 35.6, S 36.12, Pb 1.15, Ca 9.29.The arsenic sulfide slag distills at 10-100Pa and 450 DEG C after removing a small amount of sulphur and arsenic oxide arsenoxide, so that it may pure required for obtaining Arsenones experimental raw.
Following embodiment is intended to illustrate invention rather than limitation of the invention further.
Embodiment 1
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 550 DEG C.System is evacuated to after reaction 25Pa persistently distills 60min at 500 DEG C, and collection obtains condensate elemental arsenic 0.587g, and the arsenic rate of recovery is 96.39%;Through EDS It characterizes purity and is greater than 99%.
Embodiment 2
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 600 DEG C.System is evacuated to after reaction 25Pa, 90min is persistently distilled at 500 DEG C, and collection obtains condensate elemental arsenic 0.580g, the arsenic rate of recovery 95.24%;Through EDS table It levies purity and is greater than 99%.
Embodiment 3
2.00g arsenones are weighed, 2.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 120min at 550 DEG C.System is evacuated to after reaction 25Pa, 90min is persistently distilled at 500 DEG C, and collection obtains condensate elemental arsenic 1.165g, the arsenic rate of recovery 95.65%;Through EDS table It levies purity and is greater than 99%.
Embodiment 4
Compared with Example 1, the main distinction is, uses mesh number for the silicon of 1250 mesh ultra-fine grain diameters.
Test discovery, the arsenic rate of recovery 97.1%;It is greater than 99% through EDS characterization purity.
Embodiment 5
Compared with Example 1, the main distinction is, the temperature of vacuum distillation process is lower, specific as follows:
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 550 DEG C.System is evacuated to after reaction 25Pa, 60min is persistently distilled at 350 DEG C, and collection obtains condensate elemental arsenic 0.366g, the arsenic rate of recovery 60.90%;Through EDS table It levies purity and is greater than 99%.It compares, can react arsenones conversion Efficient Conversion into elemental arsenic, but subsequent negative pressure with embodiment 1 The temperature of distillation process is lower, and elemental arsenic does not recycle completely, and the rate of recovery is caused to decline.
Embodiment 6
Compared with Example 1, the main distinction is, the time of vacuum distillation process is lower, specific as follows:
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 550 DEG C.System is evacuated to after reaction 25Pa, 15min is persistently distilled at 500 DEG C, and collection obtains condensate elemental arsenic 0.254g, the arsenic rate of recovery 42.26%;Through EDS table It levies purity and is greater than 99%.
It compares, can react arsenones conversion Efficient Conversion into elemental arsenic, but subsequent vacuum distillation process with embodiment 1 Time it is shorter, elemental arsenic does not recycle completely, and the rate of recovery is caused to decline.
Comparative example 1 (compares) with embodiment 1
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 475 DEG C.System is evacuated to after reaction 25Pa persistently distills 60min at 500 DEG C, and collection obtains condensate 0.911g, is determined as the complete sulphur of unreacted through EDS characterization Change the mixture of arsenic and elemental arsenic, simple substance arsenic content is considerably less, is 8.58%.
Comparative example 2 (compares) with embodiment 1
1.00g arsenones are weighed, 1.00g silicon powder (300 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 30min at 550 DEG C.System is evacuated to after reaction 25Pa persistently distills 60min at 500 DEG C, and collection obtains condensate 0.641g, is determined as the complete sulphur of unreacted through EDS characterization Change the mixture of arsenic and elemental arsenic, simple substance arsenic content is 54.17%.
Comparative example 3
Compared with Example 1, the main distinction is, silicon mesh number is lower, and partial size is larger:
1.00g arsenones are weighed, 1.00g silicon powder (100 mesh) is added in corundum crucible after being sufficiently mixed grinding.It will dress Good corundum crucible is put into furnace, and normal pressure argon atmosphere is protected, reacts 90min at 550 DEG C.System is evacuated to after reaction 25Pa persistently distills 90min at 500 DEG C, and collection obtains condensate 0.855g, essentially all unreacted arsenones.

Claims (10)

1. a kind of method of arsenic sulfide slag processing co-production elemental arsenic, which is characterized in that protecting the mixture of arsenic sulfide slag, silicon Shield atmosphere, not less than 550 at a temperature of react, by reaction product through vacuum distillation, the elemental arsenic is made;
The granularity of the silicon is less than or equal to 300 mesh;
Reaction time is not less than 90min.
2. the method for arsenic sulfide slag processing co-production elemental arsenic as described in claim 1, which is characterized in that the arsenones Slag is before mixing in advance through vacuum distillation purification processes.
3. the method for arsenic sulfide slag processing co-production elemental arsenic as claimed in claim 2, which is characterized in that vacuum distillation purification The temperature for the treatment of process is 400-600 DEG C, pressure 10-400Pa.
4. the method for arsenic sulfide slag processing co-production elemental arsenic as claimed in claim 3, which is characterized in that vacuum distillation purification The time is handled not less than 1h.
5. such as the method for the described in any item arsenic sulfide slag processing co-production elemental arsenics of Claims 1 to 4, which is characterized in that institute The silicon stated is not less than the theoretical molar amount for reacting the arsenones in arsenic sulfide slag completely.
6. the method for arsenic sulfide slag processing co-production elemental arsenic as claimed in claim 5, which is characterized in that the silicon is will 1~2 times of the theoretical molar amount that arsenones in arsenic sulfide slag react completely.
7. the method for arsenic sulfide slag as described in claim 1 processing co-production elemental arsenic, which is characterized in that reaction temperature is 550-600℃。
8. the method for arsenic sulfide slag as described in claim 1 processing co-production elemental arsenic, which is characterized in that the reaction time is 90-120min。
9. the method for arsenic sulfide slag processing co-production elemental arsenic as described in claim 1, which is characterized in that vacuum distillation process Pressure be 15-25Pa;Temperature is 500-600 DEG C.
10. the method for arsenic sulfide slag processing co-production elemental arsenic as claimed in claim 9, which is characterized in that when vacuum distillation Between be not less than 60min;Preferably 60-90min.
CN201910320272.2A 2019-04-19 2019-04-19 Method for treating arsenic sulfide slag and co-producing elemental arsenic Expired - Fee Related CN109881015B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910320272.2A CN109881015B (en) 2019-04-19 2019-04-19 Method for treating arsenic sulfide slag and co-producing elemental arsenic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910320272.2A CN109881015B (en) 2019-04-19 2019-04-19 Method for treating arsenic sulfide slag and co-producing elemental arsenic

Publications (2)

Publication Number Publication Date
CN109881015A true CN109881015A (en) 2019-06-14
CN109881015B CN109881015B (en) 2020-02-14

Family

ID=66937959

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910320272.2A Expired - Fee Related CN109881015B (en) 2019-04-19 2019-04-19 Method for treating arsenic sulfide slag and co-producing elemental arsenic

Country Status (1)

Country Link
CN (1) CN109881015B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114107698A (en) * 2021-12-02 2022-03-01 扬州中天利新材料股份有限公司 Production method of high-stability high-purity arsenic

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5353575A (en) * 1976-10-26 1978-05-16 Nippon Mining Co Ltd Treating method for arsenic sulfide and apparatus thereof
CN103922294A (en) * 2014-04-05 2014-07-16 中南大学 Methods for recovering arsenic sulfide and metallic arsenic from arsenic sulfide waste residues

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5353575A (en) * 1976-10-26 1978-05-16 Nippon Mining Co Ltd Treating method for arsenic sulfide and apparatus thereof
CN103922294A (en) * 2014-04-05 2014-07-16 中南大学 Methods for recovering arsenic sulfide and metallic arsenic from arsenic sulfide waste residues

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114107698A (en) * 2021-12-02 2022-03-01 扬州中天利新材料股份有限公司 Production method of high-stability high-purity arsenic

Also Published As

Publication number Publication date
CN109881015B (en) 2020-02-14

Similar Documents

Publication Publication Date Title
CN109321755B (en) Method for removing arsenic from copper smelting smoke dust
CN107658519B (en) A kind of method of recycling waste lead acid battery lead plaster
CN106319199B (en) Pretreatment method of antimony-and arsenic-containing refractory gold ore
CN108130422A (en) A kind of method that valuable metal is extracted in steel plant's flue dust
CN110029218B (en) Comprehensive utilization method of gold mine cyanide-containing tailing slag
CN105907945A (en) Method for reduction, self vulcanization and dearsenification of refractory high-arsenic high-sulphur gold ore
KR20200053524A (en) Method for purifying waste or industrial by-products containing chlorine
CN111926187A (en) Method for comprehensively recovering selenium, mercury, lead and silver from acid sludge
CN109881015A (en) A kind of method of arsenic sulfide slag processing co-production elemental arsenic
CN111996383A (en) Method for separating arsenic from copper slag by matching high-arsenic materials
CN103922294B (en) A kind of method reclaiming red arsenic and metallic arsenic from red arsenic waste residue
CN106756038A (en) A kind of method that selenium mercury is separated in the acid mud from copper-lead-zinc smelting sulfate system
CN111826532B (en) Preparation method of simple substance arsenic
KR100791513B1 (en) Recovery method of zinc(zn) from dust generated by electric arc furnace steelmaking
CN114196828A (en) FeO-SiO based on high FeO content2Vulcanization volatilization method of tin-containing material of-CaO ternary system slag
CN103820587A (en) Method for removing arsenic from arsenic-containing iron-rich slag by volatilization
CA1213735A (en) Chlorination of copper, lead, zinc, iron, silver and gold
CN110642294A (en) Method for preparing vanadium oxychloride from blast furnace slag through low-temperature chlorination
CN110282885A (en) A kind of red mud step-by-step processing comprehensive utilization production system and technique
US3900552A (en) Preparation of highly pure titanium tetrachloride from perovskite or titanite
CN107789975B (en) Arsenic removal method for high-temperature flue gas
CN108103322B (en) Thiocarbamide and the technique for mentioning gold from difficult-treating gold mine is prepared in situ
KR100876932B1 (en) Process for recovering zinc component from electric arc furnace dust and apparatus therefor
Yi et al. Preparation of arsenic-antimony from arsenic alkali residue by calcification transformation-carbonthermal reduction
KR101780473B1 (en) Recovering method of valuable metal from used denitration catalyst, manufacturing method of ferroalloy and ferroalloy manufactured thereby

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for 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

Granted publication date: 20200214

CF01 Termination of patent right due to non-payment of annual fee