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CN100488890C - Method for reclaiming valuable element from acidic arsenic-containing biological oxidation gold extraction waste liquor - Google Patents

Method for reclaiming valuable element from acidic arsenic-containing biological oxidation gold extraction waste liquor Download PDF

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CN100488890C
CN100488890C CNB200710011170XA CN200710011170A CN100488890C CN 100488890 C CN100488890 C CN 100488890C CN B200710011170X A CNB200710011170X A CN B200710011170XA CN 200710011170 A CN200710011170 A CN 200710011170A CN 100488890 C CN100488890 C CN 100488890C
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gold extraction
extraction waste
iron
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CN101041498A (en
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田彦文
阎铁石
高金昌
郭普金
具滋范
阎增范
金世斌
李建中
张心新
左玉明
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LIAONING TIANLI GOLD INDUSTRY Co Ltd
Changchun Gold Research Institute
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LIAONING TIANLI GOLD INDUSTRY Co Ltd
Changchun Gold Research Institute
Northeastern University China
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Abstract

一种从酸性含砷生物氧化提金废液中回收有价元素的方法,同时向反应釜内加入酸性含砷生物氧化提金废液和沉淀剂,通过选择性沉淀,实现砷铁分离;采用过滤技术实现固液分离,固相进入铁红制备工序,液体进入回收砷的工序;回收砷后的溶液用碱液调至中性,0~4℃冷凝结晶出Na2SO4·10H2O;回收Na2SO4·10H2O后的尾液返回第1步工序,用以配制碱溶液。本发明的有益效果:实现酸性含砷生物氧化提金废液的砷、铁有效分离和砷、铁、硫分别回收利用,全流程零排放,无二次污染;酸性含砷生物氧化提金废液实现无害化、资源化综合治理。A method for recovering valuable elements from acidic arsenic-containing bio-oxidation gold extraction waste liquid, simultaneously adding acidic arsenic-containing bio-oxidation gold extraction waste liquid and a precipitant to the reaction kettle, and realizing the separation of arsenic and iron through selective precipitation; Filtration technology realizes solid-liquid separation, the solid phase enters the iron red preparation process, and the liquid enters the arsenic recovery process; after the arsenic recovery, the solution is adjusted to neutrality with lye, and Na 2 SO 4 ·10H 2 O is condensed and crystallized at 0-4°C ; The tail liquid after recovering Na 2 SO 4 ·10H 2 O is returned to the first step to prepare the alkali solution. Beneficial effects of the present invention: realize effective separation of arsenic and iron from acidic arsenic-containing biooxidation gold extraction waste liquid, and separate recycling of arsenic, iron, and sulfur, zero discharge in the whole process, and no secondary pollution; acidic arsenic-containing biooxidation gold extraction waste The liquid realizes harmless and resource-based comprehensive treatment.

Description

从酸性含砷生物氧化提金废液中回收有价元素的方法 Method for recovering valuable elements from acidic arsenic-containing biological oxidation gold extraction waste liquid

技术领域 technical field

本发明涉及从酸性含砷生物氧化提金废液中提取有价元素的一种技术。The invention relates to a technology for extracting valuable elements from acidic arsenic-containing biological oxidation gold extraction waste liquid.

背景技术 Background technique

目前国内已建成采用生物氧化提金技术的生产厂有多家,成为世界上建有生物氧化提金厂最多的国家。At present, there are many domestic production plants using bio-oxidation gold extraction technology, becoming the country with the most bio-oxidation gold extraction plants in the world.

但是,生物氧化提金工艺中产生大量含砷酸性生物氧化提金废液,这类生物氧化液pH值0.6~1.8,依所处理矿物原料的矿物组成及氧化条件不同,每m3氧化液可含(25—45)kg铁和8kg左右的砷和铜、锌、铅等少量元素。砷的化合物是一种原生质毒物,具有广泛的生物效应,已被国际防癌研究机构确定为第一类致癌物。However, a large amount of arsenic-containing acidic bio-oxidation gold-extraction waste liquid is produced in the bio-oxidation gold extraction process. The pH value of this type of biological oxidation liquid is 0.6 to 1.8 . Contains (25-45) kg of iron and about 8 kg of arsenic and a small amount of elements such as copper, zinc, and lead. Arsenic compounds are protoplasmic poisons with a wide range of biological effects, and have been identified as the first class of carcinogens by the International Agency for Cancer Research.

目前处理酸性含砷生物氧化提金废液较为成功的方法为“石灰铁盐法”,即在Fe/As大于3的条件下,以石灰进行中和处理,使As生成较稳定的FeAsO4沉淀从溶液中除去。但是在生物氧化液提金废中还存在Fe2+,致使“中和渣”里的砷不能完全以FeAsO4存在,而是部分以Ca(AsO3)2的形式存在。这类含砷的盐随土壤条件的变化,加之细菌的作用,溶解度增加,会造成明显的二次污染。更主要的是采用“石灰铁盐中和沉淀法”进行无害化处理时,需要消耗大量的石灰,处理1吨金精矿消耗石灰300~400Kg,若日处理100吨金精矿,产生的生物氧化提金废液以“石灰铁盐法”进行无害化处理时,则需日消耗石灰30~40吨,且产生约120吨左右中和渣,那么每年则产生4万吨左右的中和渣,渣量如此之大,外运必将耗费大量人力、财力,增加黄金生产成本。此外,这些含砷中和渣放于尾矿库中,也是潜在的污染源。同时,酸性含砷生物氧化提金废液中的砷、铁、硫等有价元素又白白地扔掉。日处理金精矿100吨的生物氧化提金厂日排酸性生物氧化提金废液500—600m3,每年白白扔掉近1400~1700吨砷和4000—8000吨铁,造成很大的资源浪费。要将这些有价元素回收,制成高附加值的产品,会产生可观的经济效益。At present, the more successful method for treating acidic arsenic-containing bio-oxidation gold extraction waste liquid is the "lime-iron salt method", that is, under the condition of Fe/As greater than 3, neutralize with lime, so that As can form a relatively stable FeAsO 4 precipitation Remove from solution. However, there is still Fe 2+ in the gold extraction waste of the biological oxidation solution, so that the arsenic in the "neutralization slag" cannot completely exist as FeAsO 4 , but partly exists in the form of Ca(AsO 3 ) 2 . The solubility of this kind of arsenic-containing salt increases with the change of soil conditions and the action of bacteria, which will cause obvious secondary pollution. More importantly, when using the "lime-iron-salt neutralization precipitation method" for harmless treatment, a large amount of lime needs to be consumed. 1 ton of gold concentrate consumes 300-400Kg of lime. If 100 tons of gold concentrate is processed daily, the resulting When bio-oxidation gold extraction waste liquid is harmlessly treated by "lime iron salt method", it needs to consume 30-40 tons of lime per day and produce about 120 tons of neutralized slag, so about 40,000 tons of neutralized slag will be produced every year. And slag, such a large amount of slag, Sinotrans will consume a lot of manpower and financial resources, and increase the cost of gold production. In addition, these arsenic-containing neutralized slags are placed in the tailings pool, which is also a potential source of pollution. At the same time, valuable elements such as arsenic, iron and sulfur in the acidic arsenic-containing biological oxidation gold extraction waste liquid are thrown away in vain. The bio-oxidation gold extraction plant that processes 100 tons of gold concentrate daily discharges 500-600m 3 of acidic bio-oxidation gold extraction waste liquid, and throws away nearly 1400-1700 tons of arsenic and 4000-8000 tons of iron every year, resulting in a great waste of resources . To recover these valuable elements and make them into high value-added products will produce considerable economic benefits.

发明内容 Contents of the invention

针对现有酸性生物氧化提金废液处理技术的不足之处,本发明提供一种以化学法为依托,辅以外场作用,从酸性含砷生物氧化提金废液中回收有价元素的方法,本方法能使酸性含砷生物氧化提金废液达到无害化,并实现资源综合利用和黄金生产流程零排放,降低黄金生产成本,提高经济效益。Aiming at the deficiencies of the existing acidic bio-oxidation gold extraction waste liquid treatment technology, the present invention provides a method for recovering valuable elements from the acidic arsenic-containing bio-oxidation gold extraction waste liquid based on chemical methods and supplemented by external field effects , the method can make the acidic arsenic-containing biological oxidation gold extraction waste liquid harmless, and realize the comprehensive utilization of resources and zero discharge in the gold production process, reduce the gold production cost, and improve economic benefits.

本发明为解决酸性生物氧化提金废液处理技术问题,所采用的技术方案是:酸性含砷生物氧化提金废液作为处理对象,该废液中含有Fe、As、Zn、Cu、Pb、S等元素,其含量分别为25~45g·L-1Fe,2~9g·L-1As,0.1~0.3g·L-1Zn,0.01~0.07g·L-1Cu,0.02~0.03g·L-1Pb,12~30g·L-1S,其中硫和砷分别以硫酸根和砷酸根的形式存在,铁多数以Fe3+形式存在,生物氧化提金废液pH值0.6~1.8。In order to solve the technical problem of acidic biological oxidation gold extraction waste liquid treatment, the technical scheme adopted is: the acidic arsenic-containing biological oxidation gold extraction waste liquid is used as the treatment object, and the waste liquid contains Fe, As, Zn, Cu, Pb, S and other elements, the contents of which are 25~45g·L -1 Fe, 2~9g·L -1 As, 0.1~0.3g·L -1 Zn, 0.01~0.07g·L -1 Cu, 0.02~0.03g ·L -1 Pb, 12~30g·L -1 S, in which sulfur and arsenic exist in the form of sulfate and arsenate respectively, most of iron exists in the form of Fe 3+ , and the pH value of bio-oxidation gold extraction waste liquid is 0.6~1.8 .

鉴于上述条件,提取有价元素的工艺过程是:In view of the above conditions, the process of extracting valuable elements is:

1、同时向反应釜内加入酸性含砷生物氧化提金废液和沉淀剂,该沉淀剂可以是6~10mol·L-1碱溶液,也可以是尿素,在反应釜内体系pH值为9~14、反应温度为10~60℃、搅拌强度为600~800r/min之条件下通过选择性沉淀,实现砷铁分离;1. At the same time, add acidic arsenic-containing biological oxidation gold extraction waste liquid and precipitant to the reactor. The precipitant can be 6-10mol·L -1 alkali solution or urea. The pH value of the system in the reactor is 9 ~14. Under the conditions of reaction temperature 10~60℃ and stirring intensity 600~800r/min, the separation of arsenic and iron can be realized through selective precipitation;

若采用NaOH为沉淀剂,主要反应为Fe3++3(OH-1)=Fe(OH)3If NaOH is used as precipitant, the main reaction is Fe 3+ +3(OH -1 )=Fe(OH) 3

2、采用过滤或离心分离等技术实现固液分离后,固相进入铁红制备工序,液体进入回收砷的工序;2. After solid-liquid separation is achieved by filtration or centrifugal separation, the solid phase enters the iron red preparation process, and the liquid enters the arsenic recovery process;

3、铁沉淀物经水洗后在空气气氛中焙烧1~2小时(温度范围500~900℃),得到铁红;3. After the iron precipitate is washed with water, it is roasted in the air atmosphere for 1-2 hours (temperature range 500-900°C) to obtain iron red;

4、同时向硫化沉砷反应釜内加入经过固液分离后的含砷液体、浓度为1~2mol·L-1硫化钠溶液和浓度为3~4mol·L-1硫酸溶液,在pH值为0.5~3、搅拌强度为300~500r/min、磁场强度为0.2~0.5T或不加磁场之条件下,通过硫化沉淀反应回收砷,初级产品可为雄黄或雌黄;进一步可通过湿法还原反应制备单质砷;4. At the same time, add arsenic-containing liquid with a concentration of 1 to 2 mol·L -1 sodium sulfide solution and a concentration of 3 to 4 mol·L 0.5~3, the stirring intensity is 300~500r/min, the magnetic field strength is 0.2~0.5T or no magnetic field is added, the arsenic is recovered through sulfidation precipitation reaction, and the primary product can be realgar or orpiment; further, it can be reduced by wet method Preparation of elemental arsenic;

5、回收砷后的溶液以4mol·L-1的NaOH溶液调至中性,0~4℃冷凝结晶出Na2SO4·10H2O;5. The solution after recovering arsenic is adjusted to neutrality with 4mol L -1 NaOH solution, and Na 2 SO 4 10H 2 O is condensed and crystallized at 0-4°C;

6、回收Na2SO4后的尾液返回第1步工序,用以配制碱溶液,实现全流程零排放。6. The tail liquid after recovering Na 2 SO 4 is returned to the first step to prepare the alkali solution to achieve zero discharge in the whole process.

本发明的有益效果是:The beneficial effects of the present invention are:

1、实现酸性含砷生物氧化提金废液的砷、铁有效分离和砷、铁、硫分别回收利用,砷、铁、硫的回收率均96%以上;1. Realize the effective separation of arsenic and iron from acidic arsenic-containing biological oxidation gold extraction waste liquid and the separate recycling of arsenic, iron and sulfur. The recovery rates of arsenic, iron and sulfur are all above 96%;

2、全流程零排放,无二次污染;2. Zero discharge in the whole process, no secondary pollution;

3、酸性含砷生物氧化提金废液实现无害化、资源化综合治理,使“生物氧化提金技术”的工艺更完善。避免原工艺中“石灰铁盐法”处理酸性含砷生物氧化提金废液石灰消耗量大、渣量大、有潜在污染源、白白扔掉有价元素造成资源浪费等缺点。3. The acidic arsenic-containing biological oxidation gold extraction waste liquid realizes harmless and resource-based comprehensive treatment, which makes the process of "biological oxidation gold extraction technology" more perfect. Avoid the shortcomings of the original process of "lime iron salt method" in the treatment of acidic arsenic-containing biological oxidation gold extraction waste liquid, such as large lime consumption, large amount of slag, potential pollution sources, and waste of resources caused by valuable elements being thrown away in vain.

附图说明 Description of drawings

图1为从酸性含砷生物氧化提金废液中提取有价元素的工艺流程图;Fig. 1 is a process flow diagram for extracting valuable elements from acidic arsenic-containing biological oxidation gold extraction waste liquid;

具体实施方式 Detailed ways

例1example 1

1、以每天处理250m3生物氧化提金废液(主要元素Fe含量为24g/L,As含量为5g/L)为例,其有价元素的回收工艺过程是:碱为药剂,配制8mol·L-1的碱溶液作为沉淀剂,同时向反应釜内加入酸性含砷生物氧化提金废液和沉淀剂,调整生物氧化液流速为10.5m3/h,沉淀剂流速约为5.6m3/h,并以控制反应釜内pH=12.5为准,随时调整沉淀剂流速,反应温度10℃,搅拌强度500rpm/min进行砷铁分离;1. Taking the treatment of 250m 3 bio-oxidation gold extraction waste liquid every day (the main element Fe content is 24g/L, As content is 5g/L) as an example, the recovery process of its valuable elements is: alkali is used as a medicament, and 8mol· L -1 alkaline solution is used as a precipitant, and at the same time, add acidic arsenic-containing bio-oxidation gold extraction waste liquid and a precipitant to the reactor, adjust the flow rate of the biological oxidation solution to 10.5m 3 /h, and the flow rate of the precipitant to about 5.6m 3 / h, and subject to controlling pH=12.5 in the reactor, adjust the flow rate of the precipitant at any time, the reaction temperature is 10°C, and the stirring intensity is 500rpm/min to separate arsenic and iron;

2、采用过滤或离心分离技术,进行固液分离,固相进入铁红制备工序,含砷液体进入回收砷工序;2. Use filtration or centrifugal separation technology to separate solid and liquid, the solid phase enters the iron red preparation process, and the arsenic-containing liquid enters the arsenic recovery process;

3、固相沉淀物经水洗烘干后,在500℃温度条件下空气气氛中焙烧1小时,得铁红;3. After the solid phase precipitate is washed and dried with water, it is roasted in an air atmosphere at 500°C for 1 hour to obtain iron red;

4、所得含砷液体进入砷回收工序,将含砷液体、3mol·L-1浓度的硫酸、1mol·L-1浓度的硫化钠三种液体同时加入到硫化沉砷反应釜内,含砷液体基本流量为15m3/h,含砷液体:浓硫酸:硫化钠流速比控制为10:1:1,适当调整硫酸液的流速,控制反应体系内的pH=0.5~1,搅拌强度300r/min,磁场强度0.2T或不加磁场,进行硫化沉淀,从反应釜流出来的液体通过固液分离,砷以硫化物回收,此时得到初级产品为雄黄或雌黄;4. The obtained arsenic-containing liquid enters the arsenic recovery process. The three liquids including the arsenic-containing liquid, sulfuric acid with a concentration of 3mol L -1 and sodium sulfide with a concentration of 1mol L -1 are simultaneously added to the arsenic-precipitation reaction kettle. The basic flow rate is 15m 3 /h, the flow rate ratio of arsenic-containing liquid: concentrated sulfuric acid: sodium sulfide is controlled as 10:1:1, the flow rate of sulfuric acid solution is adjusted appropriately, the pH in the reaction system is controlled to be 0.5~1, and the stirring intensity is 300r/min , the magnetic field strength is 0.2T or no magnetic field is added, carry out sulfidation precipitation, the liquid flowing out from the reaction kettle is separated by solid-liquid, arsenic is recovered with sulfide, and the primary product obtained at this time is realgar or orpiment;

5、回收砷后的溶液加4mol·L-1浓度的NaOH溶液,调至中性,0℃冷凝结晶2h,得Na2SO4·10H2O,再经加热,得无水硫酸钠;5. Add 4 mol·L -1 NaOH solution to the recovered arsenic solution, adjust to neutral, condense and crystallize at 0°C for 2 hours to obtain Na 2 SO 4 ·10H 2 O, and then heat to obtain anhydrous sodium sulfate;

6、回收Na2SO4后的尾液,返回第1步工序,用以配制碱溶液,实现全流程零排放。6. The tail liquid after recovering Na 2 SO 4 is returned to the first step to prepare the alkali solution to achieve zero discharge in the whole process.

例2Example 2

1、以每天处理500m3生物氧化提金废液(主要元素Fe含量为36g/L,As含量为7.5g/L)为例,其有价元素的回收工艺过程是:碱为药剂,配制10mol·L-1的碱溶液作为沉淀剂,同时向反应釜内加入酸性含砷生物氧化提金废液和沉淀剂,调整生物氧化液流速为21m3/h,沉淀剂流速约为11m3/h,并以控制反应釜内pH=13.5为准,随时调整沉淀剂流速,反应温度40℃,搅拌强度700rpm/min进行砷铁分离;1. Taking the treatment of 500m 3 bio-oxidation gold extraction waste liquid every day (the main element Fe content is 36g/L, As content is 7.5g/L) as an example, the recovery process of its valuable elements is: alkali is used as a drug, and 10mol ·L -1 alkaline solution is used as precipitant, and acid arsenic-containing biological oxidation gold extraction waste liquid and precipitant are added to the reactor at the same time, and the flow rate of biological oxidation solution is adjusted to 21m 3 /h, and the flow rate of precipitant is about 11m 3 /h , and based on the control of pH=13.5 in the reactor, adjust the flow rate of the precipitant at any time, the reaction temperature is 40°C, and the stirring intensity is 700rpm/min for the separation of arsenic and iron;

2、采用过滤或离心分离技术,进行固液分离,固相进入铁红制备工序,含砷液体进入回收砷工序;2. Use filtration or centrifugal separation technology to separate solid and liquid, the solid phase enters the iron red preparation process, and the arsenic-containing liquid enters the arsenic recovery process;

3、固相沉淀物经水洗烘干后,在700℃温度条件下空气气氛中焙烧1小时,得铁红;3. After the solid-phase precipitate is washed and dried, it is roasted in an air atmosphere at 700°C for 1 hour to obtain iron red;

4、所得含砷液体进入砷回收工序,将含砷液体、3.5mol·L-1浓度的硫酸、1.5mol·L-1浓度的硫化钠三种液体同时加入到硫化沉砷反应釜内,含砷液体基本流量为25m3/h,含砷液体:浓硫酸:硫化钠流速比控制为10:1:1.1,适当调整硫酸液的流速,控制反应体系内的pH=1~2,搅拌强度400r/min,磁场强度0.3T或不加磁场,进行硫化沉淀,从反应釜流出来的液体通过固液分离,砷以硫化物回收,此时得到初级产品为雄黄或雌黄;4. The obtained arsenic-containing liquid enters the arsenic recovery process, and the three liquids including the arsenic-containing liquid, sulfuric acid with a concentration of 3.5 mol L -1 and sodium sulfide with a concentration of 1.5 mol L The basic flow rate of arsenic liquid is 25m 3 /h, the flow rate ratio of arsenic liquid:concentrated sulfuric acid:sodium sulfide is controlled as 10:1:1.1, the flow rate of sulfuric acid liquid is adjusted appropriately, the pH in the reaction system is controlled to be 1~2, and the stirring intensity is 400r /min, magnetic field intensity 0.3T or no magnetic field, carry out sulfide precipitation, the liquid flowing out from the reactor is separated by solid-liquid, arsenic is recovered with sulfide, and the primary product obtained at this time is realgar or orpiment;

5、回收砷后的溶液加4mol·L-1浓度的NaOH溶液,调至中性,2℃冷凝结晶2h,得Na2SO4·10H2O,再经加热,得无水硫酸钠;5. Add 4mol·L -1 NaOH solution to the recovered arsenic solution, adjust to neutral, condense and crystallize at 2°C for 2 hours to obtain Na 2 SO 4 ·10H 2 O, and then heat to obtain anhydrous sodium sulfate;

6、回收Na2SO4后的尾液,返回第1步工序,用以配制碱溶液,实现全流程零排放。6. The tail liquid after recovering Na 2 SO 4 is returned to the first step to prepare the alkali solution to achieve zero discharge in the whole process.

例3Example 3

以每天处理500m3生物氧化废液(主要元素Fe含量为45g/L,As含量为8.5g/L)为例。其有价元素的回收工艺过程是:碱为药剂,配制10mol·L-1的碱溶液作为沉淀剂。同时向反应釜内加入酸性含砷生物氧化提金废液和沉淀剂,调整生物氧化液流速为21m3/h,沉淀剂流速约为12m3/h,并以控制反应釜内pH=13.5为准,随时调整沉淀剂流速,反应温度60℃,搅拌强度800rpm/min,进行砷铁分离;Take the treatment of 500m 3 biological oxidation waste liquid every day (the main element Fe content is 45g/L, As content is 8.5g/L) as an example. The recovery process of the valuable elements is as follows: the alkali is used as the medicine, and a 10mol·L -1 alkali solution is prepared as the precipitating agent. At the same time, add acidic arsenic-containing biological oxidation gold extraction waste liquid and precipitant to the reactor, adjust the flow rate of biological oxidation solution to be 21m 3 /h, and the flow rate of precipitant to be about 12m 3 /h, and control the pH in the reactor to be 13.5 Accurate, adjust the flow rate of the precipitant at any time, the reaction temperature is 60°C, the stirring intensity is 800rpm/min, and the arsenic and iron are separated;

2、采用过滤或离心分离技术,进行固液分离,固相进入铁红制备工序,含砷液体进入回收砷工序;2. Use filtration or centrifugal separation technology to separate solid and liquid, the solid phase enters the iron red preparation process, and the arsenic-containing liquid enters the arsenic recovery process;

3、固相沉淀物经水洗烘干后,在900℃温度条件下空气气氛中焙烧2小时,得铁红;3. After the solid-phase precipitate is washed and dried, it is roasted in an air atmosphere at 900°C for 2 hours to obtain iron red;

4、所得含砷液体进入砷回收工序,将含砷液体、4mol·L-1浓度的硫酸、2mol·L-1浓度的硫化钠三种液体同时加入到硫化沉砷反应釜内,含砷液体基本流量为31m3/h,含砷液体:浓硫酸:硫化钠流速比控制为10:1:1.2,适当调整硫酸液的流速,控制反应体系内的pH=2~3,搅拌强度500r/min,磁场强度0.5T或不加磁场,进行硫化沉淀。从反应釜流出来的液体通过固液分离,砷以硫化物回收,此时得到初级产品为雄黄或雌黄;4. The obtained arsenic-containing liquid enters the arsenic recovery process, and the three liquids including the arsenic-containing liquid, sulfuric acid with a concentration of 4mol L -1 and sodium sulfide with a concentration of 2mol L -1 are simultaneously added to the sulfide arsenic precipitation reactor, and the arsenic-containing liquid The basic flow rate is 31m 3 /h, the flow rate ratio of arsenic-containing liquid: concentrated sulfuric acid: sodium sulfide is controlled as 10:1:1.2, the flow rate of sulfuric acid solution is adjusted appropriately, the pH in the reaction system is controlled to be 2~3, and the stirring intensity is 500r/min , The magnetic field strength is 0.5T or no magnetic field is applied for sulfuration precipitation. The liquid flowing out from the reaction kettle is separated from the solid and liquid, and the arsenic is recovered as sulfide, and the primary product obtained at this time is realgar or orpiment;

5、回收砷后的溶液加4mol·L-1浓度的NaOH溶液,调至中性,4℃冷凝结晶2h,得Na2SO4·10H2O,再经加热,得无水硫酸钠;5. Add 4 mol·L -1 NaOH solution to the solution after recovery of arsenic, adjust to neutral, condense and crystallize at 4°C for 2 hours to obtain Na 2 SO 4 ·10H 2 O, and then heat to obtain anhydrous sodium sulfate;

6、回收Na2SO4后的尾液,返回第1步工序,用以配制碱溶液,实现全流程零排放。6. The tail liquid after recovering Na 2 SO 4 is returned to the first step to prepare the alkali solution to achieve zero discharge in the whole process.

Claims (1)

1, a kind of method that reclaims valuable element from acidic arsenic-containing biological oxidation gold extraction waste liquor is characterized in that may further comprise the steps:
1) add acidic arsenic-containing biological oxidation gold extraction waste liquor and precipitation agent, simultaneously in reactor, this precipitation agent is 6~10molL -1Alkaline solution or urea, system pH is 9~14 in the control reactor, temperature of reaction is 10~60 ℃, at stirring intensity be under the condition of 600~800r/min by selective precipitation, realize that arsenic iron separates;
2), adopt to filter or centrifugal separation technique is realized solid-liquid separation, separate the back solid phase and enter the iron oxide red preparation section, liquid enters the operation that reclaims arsenic;
3), iron precipitate roasting 1~2 hour in air atmosphere after washing, maturing temperature is 500~900 ℃, obtains iron oxide red;
4), in the heavy arsenic reactor of sulfuration, add simultaneously through after the solid-liquid separation contain arsenic liquid, concentration is 1~2molL -1Sodium sulfide solution and concentration are 3~4molL -1Sulphuric acid soln is 0.5~3 in the pH value, stirring intensity is that 300~500r/min, magneticstrength are 0.2~0.5T or do not add under the condition in magnetic field, reclaims arsenic by the sulfide precipitation reaction, and primary products are realgar or orpiment; In order to further passing through wet reducing prepared in reaction elemental arsenic;
5), the solution behind the recovery arsenic is with 4molL -1NaOH solution transfer to neutrality, 0~4 ℃ of condensation-crystallization goes out Na 2SO 410H 2O;
6), reclaim Na 2SO 4After tail washings return the 1st step operation, in order to the preparation alkaline solution, realize the whole process zero release.
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