CN106636678B - A kind of method that arsenic-containing material direct-reduction roasting prepares arsenic - Google Patents
A kind of method that arsenic-containing material direct-reduction roasting prepares arsenic Download PDFInfo
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Abstract
本发明公开了一种含砷物料直接还原焙烧制备砷的方法,该方法以砷酸盐为原料,砷酸盐物料与碳质还原剂混合均匀后,置于惰性或还原气氛中,在负压条件下,进行还原焙烧,收集焙烧烟气,即得砷产品。该方法使冶金过程中常见的以砷酸盐为主的含砷物料还原为化学稳定的单质砷,单质砷不仅无毒且可以作为半导体和合金工业的原料,具有一定的市场价值,还原过程实现了有毒含砷物料的减量化、无害化和资源化,是砷最为合理的走向,极具推广价值。The invention discloses a method for preparing arsenic by directly reducing and roasting arsenic-containing materials. The method uses arsenate as a raw material, and after the arsenate material is uniformly mixed with a carbonaceous reducing agent, it is placed in an inert or reducing atmosphere, and the Under certain conditions, reduction roasting is carried out, and roasting flue gas is collected to obtain arsenic products. This method reduces the common arsenate-containing arsenic materials in the metallurgical process to chemically stable elemental arsenic. Elemental arsenic is not only non-toxic but also can be used as a raw material for semiconductor and alloy industries, and has certain market value. The reduction process realizes It is the most reasonable direction for arsenic to realize the reduction, harmlessness and recycling of toxic arsenic-containing materials, and it is of great promotion value.
Description
技术领域technical field
本发明涉及一种由含砷物料制备砷的方法,特别涉及一种含砷酸盐物料直接通过还原焙烧制备砷的方法,属于有色金属冶金技术领域。The invention relates to a method for preparing arsenic from arsenic-containing materials, in particular to a method for directly preparing arsenic from arsenic-containing materials through reduction roasting, and belongs to the technical field of nonferrous metal metallurgy.
技术背景technical background
有色冶炼过程中产生的碱渣、烟灰和阳极泥等物料中多含有砷,当采用湿法过程进行处理和净化时,脱砷工艺必不可少。采用碱性条件浸出,再进行结晶或沉淀分离是一种有效和常见的脱砷方法,但该过程产生大量的砷酸盐,这些砷酸盐有毒且化学性质不稳定,容易对环境和人体健康造成威胁,因此需要找到一种经济环保的方法对砷酸盐进行后续处理。The alkali slag, soot and anode slime produced in the non-ferrous smelting process often contain arsenic. When the wet process is used for treatment and purification, the arsenic removal process is essential. Leaching under alkaline conditions, followed by crystallization or precipitation separation is an effective and common method for arsenic removal, but this process produces a large amount of arsenate, which is toxic and chemically unstable, and is likely to be harmful to the environment and human health. posed a threat, it was therefore necessary to find an economical and environmentally friendly method for subsequent disposal of arsenate.
对于这类砷酸盐的处理,目前主要采用固化的方法,常用的固化方法有水泥固化、石灰固化、塑料固化、沥青固化、熔融固化等,虽然能够在一定程度上实现砷的固定,但这些固化方法均存在固化前后增容比大、后期需要大量土地堆存和填埋等问题。For the treatment of this kind of arsenate, the method of solidification is mainly adopted at present. The common solidification methods include cement solidification, lime solidification, plastic solidification, asphalt solidification, melt solidification, etc. Although arsenic can be fixed to a certain extent, these The curing methods all have the problems of large volume increase ratio before and after curing, and the need for a large amount of land stockpiling and landfilling in the later stage.
目前,金属砷的生产一般都是将含砷的矿石先通过氧化焙烧回收砷的氧化物,再以砷的氧化物为原料,以氢气、碳等作为还原剂进行还原反应而得到,未见有直接还原砷酸盐的报道。At present, the production of metal arsenic is generally obtained by oxidizing and roasting arsenic-containing ores first to recover arsenic oxides, and then using arsenic oxides as raw materials, and using hydrogen, carbon, etc. as reducing agents to carry out reduction reactions. A report on the direct reduction of arsenate.
发明内容Contents of the invention
为解决现有含砷物料,尤其是砷酸盐物料的难处理问题,本发明的目的是旨在提供一种清洁、高效的从含砷物料中直接回收高纯度砷的方法,该方法实现了含砷废渣的减量化、无害化和资源化。In order to solve the difficult problem of existing arsenic-containing materials, especially arsenate materials, the purpose of the present invention is to provide a clean and efficient method for directly recovering high-purity arsenic from arsenic-containing materials, which realizes Reduction, harmlessness and recycling of arsenic-containing waste residues.
为了实现上述技术目的,本发明提供了一种含砷物料直接还原焙烧制备砷的方法,砷酸盐物料与碳质还原剂混合后,置于惰性或还原气氛中,在负压及≥600℃温度条件下进行还原焙烧,收集焙烧烟气,即得砷产品。In order to achieve the above technical purpose, the present invention provides a method for preparing arsenic by direct reduction and roasting of arsenic-containing materials. After the arsenate material is mixed with a carbonaceous reducing agent, it is placed in an inert or reducing atmosphere. Reduction roasting is carried out under temperature conditions, and roasting flue gas is collected to obtain arsenic products.
优选的方案,所述砷酸盐物料与所述碳质还原剂的比例以砷与碳的摩尔比为1:(0.5~5)计量。In a preferred solution, the ratio of the arsenate material to the carbonaceous reducing agent is measured by a molar ratio of arsenic to carbon of 1:(0.5-5).
较优选的方案,砷酸盐物料包括砷酸钠、砷酸钙、砷酸铅、砷酸钡、砷酸镁、砷酸铁中的至少一种。More preferably, the arsenate material includes at least one of sodium arsenate, calcium arsenate, lead arsenate, barium arsenate, magnesium arsenate and iron arsenate.
较优选的方案,碳质还原剂包括石焦油粉、焦炭粉、活性炭粉、碳黑粉、石墨粉和木炭粉中的至少一种。More preferably, the carbonaceous reducing agent includes at least one of petroleum tar powder, coke powder, activated carbon powder, carbon black powder, graphite powder and charcoal powder.
优选的方案,所述负压的真空度为0.1~101325Pa。In a preferred solution, the vacuum degree of the negative pressure is 0.1-101325Pa.
优选的方案,还原焙烧温度较优选为700~1200℃,更优选还原焙烧温度为700~900℃。In a preferred solution, the reduction calcination temperature is more preferably 700-1200°C, and more preferably the reduction calcination temperature is 700-900°C.
优选的方案,还原焙烧时间为1~8h;更优选的还原焙烧时间为2~4h。In a preferred scheme, the reduction roasting time is 1-8 hours; the more preferred reduction roasting time is 2-4 hours.
优选的方案,砷产品品位大于90%;更优选为品位大于94%。In a preferred solution, the grade of the arsenic product is greater than 90%; more preferably, the grade is greater than 94%.
本发明的技术方案中采用的还原气氛主要为惰性气体和/或氮气与氢气和/或一氧化碳等的混合气氛。The reducing atmosphere adopted in the technical solution of the present invention is mainly a mixed atmosphere of inert gas and/or nitrogen and hydrogen and/or carbon monoxide.
本发明技术方案的基本原理,以及相对现有技术带来的优势:The basic principle of the technical solution of the present invention, and the advantage brought compared with the prior art:
本发明的技术方案关键是对还原焙烧中的温度、压力等条件的控制,通过发明人大量的研究表明,在本发明技术方案控制的条件下,砷酸盐物料在碳质还原剂中主要发生以下还原反应,以砷酸钠、砷酸钙及砷酸铁为例进行具体说明,发生的反应如方程(1)~(7)所示:The key to the technical solution of the present invention is the control of conditions such as temperature and pressure in the reduction roasting. A large number of studies by the inventor have shown that under the conditions controlled by the technical solution of the present invention, the arsenate material mainly occurs in the carbonaceous reducing agent. The following reduction reactions are specifically illustrated by taking sodium arsenate, calcium arsenate and iron arsenate as examples, and the reactions that occur are shown in equations (1) to (7):
4Na3AsO4+5C=5Na2CO3+As4(g)+Na2O (1)4Na 3 AsO 4 +5C=5Na 2 CO 3 +As 4 (g)+Na 2 O (1)
4Na3AsO4+5C+H2O=5Na2CO3+As4(g)+2NaOH (2)4Na 3 AsO 4 +5C+H 2 O=5Na 2 CO 3 +As 4 (g)+2NaOH (2)
4Na3AsO4+10C+6H2O(g)=12NaOH+10CO(g)+As4(g) (3)4Na 3 AsO 4 +10C+6H 2 O(g)=12NaOH+10CO(g)+As 4 (g) (3)
2Ca3(AsO4)2+5C=6CaO+5CO2(g)+As4(g) (4)2Ca 3 (AsO 4 ) 2 +5C=6CaO+5CO 2 (g)+As 4 (g) (4)
2Ca3(AsO4)2+10C=6CaO+10CO(g)+As4(g) (5)2Ca 3 (AsO 4 ) 2 +10C=6CaO+10CO(g)+As 4 (g) (5)
4FeAsO4+8C=4Fe+8CO2(g)+As4(g) (6)4FeAsO 4 +8C=4Fe+8CO 2 (g)+As 4 (g) (6)
4FeAsO4+16C=4Fe+16CO(g)+As4(g) (7)4FeAsO 4 +16C=4Fe+16CO(g)+As 4 (g) (7)
反应(1)~(7)的吉布斯自由能变化值与温度的关系如图1所示。由图1中可以看出,在本发明的工艺条件下,这些反应均能够顺利发生。The relationship between the change value of Gibbs free energy and temperature of reactions (1)-(7) is shown in Figure 1. As can be seen from Figure 1, under the process conditions of the present invention, these reactions can all take place smoothly.
与现有技术相比,本发明的有益效果是:Compared with prior art, the beneficial effect of the present invention is:
1)本发明的技术方案首次通过还原焙烧法将砷酸盐物料一步还原制备高纯度的砷产品。1) In the technical solution of the present invention, the arsenate material is reduced in one step to prepare a high-purity arsenic product for the first time by a reduction roasting method.
2)通过本发明的技术方案可以将现有的有色冶金行业大量存在的有毒砷酸盐还原为无毒的单质砷,砷产率>95%,单质砷纯度>90%,可以直接作为产品销售,同时反应前后含砷物质的体积减小,利于填埋和堆存处置;实现了砷的减量化、无害化和资源化处置,具有推广价值。2) Through the technical solution of the present invention, the toxic arsenate that exists in large quantities in the existing nonferrous metallurgy industry can be reduced to non-toxic elemental arsenic, the yield of arsenic is >95%, the purity of elemental arsenic is >90%, and it can be directly sold as a product At the same time, the volume of arsenic-containing substances before and after the reaction is reduced, which is beneficial to landfill and stockpiling disposal; the reduction, harmless and resourceful disposal of arsenic has been realized, and it has promotion value.
3)本发明的技术方案工艺条件温和,绿色环保,操作简单,有利于工业化生产。3) The technical solution of the present invention has mild process conditions, environmental protection, simple operation, and is beneficial to industrialized production.
附图说明Description of drawings
【图1】为反应(1)~(7)在常压条件下吉布斯自由能变化与温度的关系;[Figure 1] is the relationship between the change of Gibbs free energy and temperature for reactions (1)-(7) under normal pressure conditions;
具体实施方式Detailed ways
下面结合具体实例对本发明内容进一步说明,但不会限制本发明权利要求保护范围。The content of the present invention will be further described below in conjunction with specific examples, but the protection scope of the claims of the present invention will not be limited.
实施例1Example 1
以云南某铜烟灰碱浸—石灰沉淀得到的砷酸钙为原料,取原料100Kg与碳粉混合均匀后放入真空电弧炉(碳粉加入量为原料质量的15%),开启真空泵,当压力1000Pa时开始升温,升温至700℃并保持还原环境3小时后停止加热,使砷蒸汽冷凝,还原结束后,当温度降低至室温,关闭真空炉,从冷凝管段得到金属砷,经检测纯度>95%,还原渣样主要成分为CaO。Using calcium arsenate obtained from a certain copper soot alkali leaching-lime precipitation in Yunnan as raw material, take 100Kg of the raw material and mix it with carbon powder evenly and put it into a vacuum electric arc furnace (the amount of carbon powder added is 15% of the mass of the raw material), turn on the vacuum pump, when the pressure Start to heat up at 1000Pa, raise the temperature to 700°C and maintain the reducing environment for 3 hours, then stop heating to condense the arsenic vapor. After the reduction is completed, when the temperature drops to room temperature, close the vacuum furnace, and obtain metal arsenic from the condensation pipe section, the purity of which is >95 %, the main component of the reduced slag sample is CaO.
实施例2Example 2
以云南某锡电解阳极泥高压碱浸-冷却结晶得到的砷酸钠晶体为原料,该结晶含As 30.13%、Pb 0.58%、Sb 0.42%和Sn 0.07%。取100Kg该砷酸钠晶体与碳粉混合均匀后放入真空电弧炉(碳粉加入量为原料质量的20%),开启真空泵,当压力1Pa时开始升温,升温至700℃并保持还原环境4小时后停止加热,使砷蒸汽冷凝,还原结束后,当温度降低至室温,关闭真空炉,从冷凝管段得到金属砷,经检测纯度>94%,还原渣样主要成分为Na2CO3。Sodium arsenate crystals obtained by high-pressure alkali leaching-cooling crystallization of a tin electrolytic anode slime in Yunnan are used as raw materials. The crystals contain 30.13% As, 0.58% Pb, 0.42% Sb and 0.07% Sn. Take 100Kg of the sodium arsenate crystal and mix it with carbon powder and put it into a vacuum electric arc furnace (the amount of carbon powder added is 20% of the mass of the raw material), turn on the vacuum pump, start to heat up when the pressure is 1Pa, and raise the temperature to 700°C and maintain a reducing environment for 4 After 1 hour, stop heating to condense the arsenic vapor. After the reduction, when the temperature drops to room temperature, close the vacuum furnace, and obtain metallic arsenic from the condensation pipe section. The purity is >94% after testing. The main component of the reduction slag sample is Na 2 CO 3 .
实施例3Example 3
以云南某铜电解阳极泥高压碱浸-铁盐沉淀得到的砷酸铁为原料,取100Kg原料与碳粉混合均匀后放入还原电炉(碳粉加入量为原料质量的20%),升温至900℃并保持还原环境2小时后停止加热,使砷蒸汽冷凝,还原结束后,当温度降低至室温,关闭还原炉,从冷凝管段得到金属砷,经检测纯度>96%,还原渣样主要成分为Fe的氧化物。With the ferric arsenate obtained by high-pressure alkali leaching-iron salt precipitation of a certain copper electrolytic anode slime in Yunnan as raw material, 100Kg of raw material and carbon powder are mixed evenly and then put into a reduction electric furnace (the carbon powder addition is 20% of the raw material quality), and the temperature is raised to Keep the reducing environment at 900°C for 2 hours, then stop heating to condense the arsenic vapor. After the reduction, when the temperature drops to room temperature, close the reduction furnace, and obtain metallic arsenic from the condensation pipe section. The purity is >96% after testing, and the main components of the reduced slag sample It is an oxide of Fe.
对比实施例1Comparative Example 1
以云南某锡电解阳极泥高压碱浸-冷却结晶得到的砷酸钠晶体为原料,该结晶含As 30.13%、Pb 0.58%、Sb 0.42%和Sn 0.07%。取100Kg该砷酸钠晶体与碳粉混合均匀后放入真空电弧炉(碳粉加入量为原料质量的20%),开启真空泵,当压力1Pa时开始升温,升温至550℃并保持还原环境4小时后停止加热,砷主要以单质和砷酸钠的形态存在于还原渣样中,冷凝管段几乎得不到金属砷。Sodium arsenate crystals obtained by high-pressure alkali leaching-cooling crystallization of a tin electrolytic anode slime in Yunnan are used as raw materials. The crystals contain 30.13% As, 0.58% Pb, 0.42% Sb and 0.07% Sn. Take 100Kg of the sodium arsenate crystal and mix it evenly with carbon powder and put it into a vacuum electric arc furnace (the amount of carbon powder added is 20% of the mass of the raw material), turn on the vacuum pump, start to heat up when the pressure is 1Pa, raise the temperature to 550 ° C and maintain a reducing environment for 4 Stop heating after 1 hour, arsenic mainly exists in the reducing slag sample in the form of elemental substance and sodium arsenate, and metal arsenic is hardly obtained in the condensation pipe section.
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| CN109913657A (en) * | 2019-03-12 | 2019-06-21 | 济源市中亿科技有限公司 | A method of recycling lead bronze arsenic from white cigarette dirt |
| CN110184450A (en) * | 2019-05-21 | 2019-08-30 | 铜仁学院 | A method of processing arsenic scum |
| CN110229962A (en) * | 2019-05-21 | 2019-09-13 | 铜仁学院 | A kind of method of arsenic scum resource utilization |
| CN110144463A (en) * | 2019-05-21 | 2019-08-20 | 铜仁学院 | A method for resource utilization of arsenic and calcium slag |
| CN111334673B (en) * | 2020-03-13 | 2022-06-07 | 江西理工大学 | Method for selectively recovering antimony, arsenic and alkali from arsenic-alkali residue |
| CN113462907A (en) * | 2021-06-30 | 2021-10-01 | 林西金易来砷业有限公司 | Process for producing arsenic by using arsenic-containing material |
| CN114836635B (en) * | 2022-03-25 | 2023-05-16 | 中南大学 | A short-process method for preparing high-purity metal arsenic from non-ferrous smelting arsenic-containing solid waste |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102965517A (en) * | 2012-12-03 | 2013-03-13 | 中南大学 | Treatment method for vitrifying arsenic-alkali residue |
| CN103555931A (en) * | 2013-11-15 | 2014-02-05 | 湖南省环境保护科学研究院 | Method for comprehensive utilization of removed arsenium of high-arsenium-sulfur-iron watercourse tailings |
| CN103710532A (en) * | 2014-01-22 | 2014-04-09 | 安徽工业大学 | Method for performing microwave arsenic removal on high-arsenic iron ore |
| CN104451167A (en) * | 2014-11-17 | 2015-03-25 | 长沙有色冶金设计研究院有限公司 | Method for processing arsenic in high-arsenic material smelting flue gas |
| CN105907945A (en) * | 2016-04-28 | 2016-08-31 | 中南大学 | Method for reduction, self vulcanization and dearsenification of refractory high-arsenic high-sulphur gold ore |
-
2016
- 2016-11-14 CN CN201611001156.7A patent/CN106636678B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102965517A (en) * | 2012-12-03 | 2013-03-13 | 中南大学 | Treatment method for vitrifying arsenic-alkali residue |
| CN103555931A (en) * | 2013-11-15 | 2014-02-05 | 湖南省环境保护科学研究院 | Method for comprehensive utilization of removed arsenium of high-arsenium-sulfur-iron watercourse tailings |
| CN103710532A (en) * | 2014-01-22 | 2014-04-09 | 安徽工业大学 | Method for performing microwave arsenic removal on high-arsenic iron ore |
| CN104451167A (en) * | 2014-11-17 | 2015-03-25 | 长沙有色冶金设计研究院有限公司 | Method for processing arsenic in high-arsenic material smelting flue gas |
| CN105907945A (en) * | 2016-04-28 | 2016-08-31 | 中南大学 | Method for reduction, self vulcanization and dearsenification of refractory high-arsenic high-sulphur gold ore |
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