CN116640925A - Method for weakening surface passivation effect of low-grade chalcocite by using L-ascorbic acid - Google Patents
Method for weakening surface passivation effect of low-grade chalcocite by using L-ascorbic acid Download PDFInfo
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Abstract
本发明属于生物冶金技术领域,具体涉及一种利用L‑抗坏血酸减弱辉铜矿表面钝化效应的方法。所述方法是以经辉铜矿纯矿物驯化的嗜酸性氧化亚铁硫杆菌、氧化亚铁钩端螺旋菌和嗜酸性铁原体菌混合菌种为浸出菌种,生物浸出低品位辉铜矿,在浸出过程中监控浸出体系的pH值和Eh值变化情况,每间隔24h测量一次,当浸出体系的pH测量值超过1.90±0.05时加硫酸降低pH值至1.90±0.05,当浸出体系的Eh测量值超过500±5mV时加L‑抗坏血酸降低Eh值至500±5mV,浸出周期为20d,最终实现利用L‑抗坏血酸减弱低品位辉铜矿表面钝化效应、并提高低品位辉铜矿生物浸出效率。经测定,本发明Cu浸出率可达96%。The invention belongs to the technical field of biometallurgy, and in particular relates to a method for weakening the surface passivation effect of chalcocite by using L-ascorbic acid. The method uses acidophilic Thiobacillus ferrooxidans, Leptospira ferrooxidans and acidophilic ferroplasma bacteria domesticated by chalcocite pure minerals as leaching strains, and bioleaches low-grade chalcocite. , during the leaching process, monitor the pH value and Eh value of the leaching system, and measure it every 24 hours. When the pH value of the leaching system exceeds 1.90±0.05, add sulfuric acid to reduce the pH value to 1.90±0.05. When the measured value exceeds 500±5mV, add L-ascorbic acid to reduce the Eh value to 500±5mV, and the leaching cycle is 20d, and finally realize the use of L-ascorbic acid to weaken the surface passivation effect of low-grade chalcocite and improve the bioleaching of low-grade chalcocite efficiency. It has been determined that the leaching rate of Cu in the present invention can reach 96%.
Description
技术领域technical field
本发明属于生物冶金技术领域,具体涉及一种利用L-抗坏血酸减弱辉铜矿表面钝化效应的方法。The invention belongs to the technical field of biometallurgy, and in particular relates to a method for weakening the surface passivation effect of chalcocite by using L-ascorbic acid.
背景技术Background technique
黄铁矿是辉铜矿生物浸出过程中常见的伴生脉石矿物,在复杂的浸矿体系中,黄铁矿溶解生成的Fe3+会发生水解反应,生成不同形式的沉淀物,会导致浸出体系中pH值发生变化。在生物浸出过程中,水解反应会消耗硫化矿氧化所需的氧化剂Fe3+,致使微生物的能源物质—Fe2+浓度降低,影响微生物的生长活性;同时Fe3+水解生成的铁矾等沉淀物质还会附着在硫化铜表面,降低铜的溶解率,即铜矿生物浸出过程中的钝化作用。Pyrite is a common associated gangue mineral in the bioleaching process of chalcocite. In the complex leaching system, the Fe 3+ generated by the dissolution of pyrite will undergo hydrolysis reaction, and different forms of precipitates will be formed, which will lead to leaching. The pH value of the system changes. During the bioleaching process, the hydrolysis reaction will consume the oxidant Fe 3+ required for the oxidation of sulfide ore, resulting in a decrease in the concentration of Fe 2+ , the energy material for microorganisms, and affecting the growth and activity of microorganisms; at the same time, iron vitriol produced by the hydrolysis of Fe 3+ will precipitate The substance will also attach to the surface of copper sulfide, reducing the dissolution rate of copper, that is, the passivation in the process of copper ore bioleaching.
相关人员研究发现,辉铜矿生物浸出过程中矿石表面的钝化效应与浸出体系中的Eh值密切相关。在铜矿的生物浸出过程中,Eh值主要的影响因素为Fe3+、Fe2+的浓度。因此可以向浸出体系中加入还原剂,使得浸出体系中大量的Fe3+被还原成Fe2+,而被还原的Fe2+可继续作为细菌的能源物质,Fe3+继续氧化辉铜矿;此外还可以降低铁矾类物质的生成,减弱铜矿物表面的钝化作用,促进浸出反应的进行,从而提高辉铜矿的浸出率。Relevant researchers have found that the passivation effect of the ore surface during chalcocite bioleaching is closely related to the Eh value in the leaching system. In the bioleaching process of copper ore, the main influencing factors of Eh value are the concentrations of Fe 3+ and Fe 2+ . Therefore, a reducing agent can be added to the leaching system, so that a large amount of Fe 3+ in the leaching system is reduced to Fe 2+ , and the reduced Fe 2+ can continue to be used as an energy source for bacteria, and Fe 3+ continues to oxidize chalcocite; In addition, it can also reduce the formation of ferrite substances, weaken the passivation effect on the surface of copper minerals, and promote the leaching reaction, thereby increasing the leaching rate of chalcocite.
因此,申请人基于此提出了一种加入L-抗坏血酸还原剂减弱辉铜矿表面钝化效应的方法,该方法在生物浸出中期通过加入L-抗坏血酸还原剂,促使浸出体系中的Fe3+被还原为Fe2+,降低铁矾类钝化物的生成。本发明对于提高辉铜矿的生物浸出率有重要意义。Therefore, based on this, the applicant proposed a method of adding L-ascorbic acid reducing agent to weaken the surface passivation effect of chalcocite. In the middle stage of bioleaching , the Fe in the leaching system is promoted to be depleted by adding L-ascorbic acid reducing agent. Reduction to Fe 2+ , reducing the generation of passivation products such as ferrite. The invention has great significance for improving the bioleaching rate of chalcocite.
发明内容Contents of the invention
本发明的目的是为了提高辉铜矿的浸出效率,而提出一种利用L-抗坏血酸减弱辉铜矿表面钝化效应的方法,此方法能显著促进提高辉铜矿的浸出效率。The purpose of the present invention is in order to improve the leaching efficiency of chalcocite, and propose a kind of method that utilizes L-ascorbic acid to weaken the surface passivation effect of chalcocite, this method can significantly promote the leaching efficiency that improves chalcocite.
为实现上述目的,本发明采用如下技术方案:To achieve the above object, the present invention adopts the following technical solutions:
一种利用L-抗坏血酸减弱低品位辉铜矿表面钝化效应的方法,其是以经辉铜矿纯矿物驯化的嗜酸性氧化亚铁硫杆菌、氧化亚铁钩端螺旋菌和嗜酸性铁原体菌混合菌种为浸出菌种,生物浸出低品位辉铜矿,在浸出过程中监控浸出体系的pH值和Eh值变化情况,每间隔24h测量一次,当浸出体系的pH测量值超过1.90±0.05时加硫酸降低pH值至1.90±0.05,当浸出体系的Eh测量值超过500±5mV时加L-抗坏血酸降低Eh值至500±5mV,浸出周期为20d,最终实现利用L-抗坏血酸减弱低品位辉铜矿表面钝化效应、并提高低品位辉铜矿生物浸出效率。A method for using L-ascorbic acid to weaken the surface passivation effect of low-grade chalcocite, which is acidophilic Thiobacillus ferrooxidans, Leptospira ferrooxidans and acidophilic ferrogenase domesticated through chalcocite pure minerals The mixed strains of bacteria are the leaching strains, and the low-grade chalcocite is bioleached. During the leaching process, the pH value and Eh value of the leaching system are monitored and measured every 24 hours. When the pH value of the leaching system exceeds 1.90± At 0.05, add sulfuric acid to reduce the pH value to 1.90±0.05. When the measured Eh value of the leaching system exceeds 500±5mV, add L-ascorbic acid to reduce the Eh value to 500±5mV. The leaching cycle is 20d, and finally realize the use of L-ascorbic acid to weaken the low-grade Chalcocite surface passivation effect, and improve low-grade chalcocite bioleaching efficiency.
上述一种利用L-抗坏血酸减弱低品位辉铜矿表面钝化效应的方法,具体包括以下步骤:Above-mentioned a kind of method utilizing L-ascorbic acid to weaken low-grade chalcocite surface passivation effect specifically comprises the following steps:
(1)将低品位辉铜矿制为粒度≤74μm的粉末;(1) making low-grade chalcocite into powder with a particle size of ≤74 μm;
(2)将10mL铁细菌混合菌液接入90mL 9K培养基,用硫酸溶液调节pH值为1.8,放置在30℃、150r/min恒温振荡培养箱振荡培养,每6d按10vol%接种量传代一次,当培养液颜色由淡绿色变为红棕色时结束传代,得到传代培养菌液;其中,所述铁细菌混合菌液由1×107CFU/mL嗜酸性氧化亚铁硫杆菌、1×106CFU/mL氧化亚铁钩端螺旋菌及1×104CFU/mL嗜酸性铁原体菌组成;(2) Put 10mL iron bacteria mixed bacteria solution into 90mL 9K medium, adjust the pH value to 1.8 with sulfuric acid solution, place it in a constant temperature shaking incubator at 30°C and 150r/min for shaking culture, and passage once every 6 days with 10vol% inoculum , when the color of the culture solution changed from light green to reddish brown, the subculture was completed to obtain a subculture culture solution; wherein, the mixed bacteria solution of iron bacteria was composed of 1×10 7 CFU/mL acidophilic Thiobacillus ferrooxidans, 1×10 Composition of 6 CFU/mL Leptospira ferrous oxide and 1×10 4 CFU/mL acidophilic ferroplasma;
(3)取10mL步骤(2)得到的传代培养菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养至培养液变为红棕色,得到一次驯化菌液;取10mL一次驯化菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养至培养液变为红棕色,得到二次驯化菌液;(3) Take 10 mL of the subculture culture solution obtained in step (2) and put it in a 250 mL Erlenmeyer flask, put it into a constant temperature shaking incubator at a temperature of 30 °C and 150 r/min for shaking culture, and add 90 mL of no Iron 9K medium and 1.0g chalcocite pure mineral, continue to cultivate until the culture medium turns reddish-brown to obtain a primary domesticated bacterial liquid; take 10mL primary domesticated bacterial liquid and place it in a 250mL Erlenmeyer flask, put it in a temperature of 30°C and 150r Vibration culture in a constant temperature shaking incubator, when the bacteria grow to the logarithmic phase, add 90mL iron-free 9K medium and 1.0g chalcocite pure mineral, continue to cultivate until the culture medium turns reddish brown, and obtain the secondary acclimatization bacteria liquid;
(4)在250mL锥形瓶中加入2~3g步骤(1)得到的低品位辉铜矿粉末、10mL步骤(3)得到的二次驯化菌液和90mL无铁9K培养基,混合后置于40±5℃、180±10r/min恒温振荡培养箱中进行生物揺瓶浸出,整个浸出周期为20d,在浸出过程中对浸出体系的pH值和Eh值进行监控,每间隔24h测量一次,当浸出体系的pH测量值超过1.90±0.05时加硫酸溶液降低pH值至1.90±0.05,当浸出体系的Eh值超过500±5mV时加L-抗坏血酸溶液降低Eh值至500±5mV;(4) Add 2-3g of low-grade chalcocite powder obtained in step (1), 10mL of secondary domesticated bacteria liquid obtained in step (3) and 90mL of iron-free 9K medium in a 250mL Erlenmeyer flask, mix and place in 40±5℃, 180±10r/min constant temperature shaking incubator for biological bottle leaching, the whole leaching cycle is 20d, during the leaching process, the pH value and Eh value of the leaching system are monitored and measured every 24h, when When the measured pH value of the leaching system exceeds 1.90±0.05, add sulfuric acid solution to reduce the pH value to 1.90±0.05, and add L-ascorbic acid solution to reduce the Eh value to 500±5mV when the Eh value of the leaching system exceeds 500±5mV;
其中,所述低品位辉铜矿的Cu品位为0.30%±0.05%;Wherein, the Cu grade of the low-grade chalcocite is 0.30%±0.05%;
其中,所述9K培养基的配方为:A液:3.0g/L(NH)2SO4、0.5g/L K2HPO4、0.1g/L KCl、0.5g/L MgSO4·7H2O、0.01g/L Ca(NO3)2、去离子水800mL,调节pH值至2.0,121℃高压灭菌20min;B液:FeSO4·7H2O 44.3g/L、去离子水200mL,调节pH值至2.0,0.22μm滤膜过滤除菌;将灭菌后的800mLA液与200mLB液混匀后分装;Wherein, the formulation of the 9K medium is: Liquid A: 3.0g/L (NH) 2 SO 4 , 0.5g/L K 2 HPO 4 , 0.1g/L KCl, 0.5g/L MgSO 4 ·7H 2 O, 0.01g/L Ca(NO 3 ) 2 , 800mL deionized water, adjust the pH to 2.0, autoclave at 121°C for 20min; liquid B: FeSO 4 7H 2 O 44.3g/L, 200mL deionized water, adjust the pH value to 2.0, 0.22μm filter membrane filtration sterilization; after the sterilization of 800mL A liquid and 200mL of B liquid mixed and packed;
其中,所述无铁9K培养基的配方为:3.0g/L(NH)2SO4、0.5g/L K2HPO4、0.1g/L KCl、0.5g/L MgSO4·7H2O、0.01g/L Ca(NO3)2、去离子水100mL,调节pH值至2.0,121℃高压灭菌20min;Wherein, the formulation of the iron-free 9K medium is: 3.0g/L (NH) 2 SO 4 , 0.5g/L K 2 HPO 4 , 0.1g/L KCl, 0.5g/L MgSO 4 ·7H 2 O, 0.01 g/L Ca(NO 3 ) 2 , 100mL deionized water, adjust the pH value to 2.0, and autoclave at 121°C for 20min;
其中,所述硫酸溶液的浓度为50%v/v;Wherein, the concentration of the sulfuric acid solution is 50% v/v;
其中,所述L-抗坏血酸溶液的浓度为100g/L。Wherein, the concentration of the L-ascorbic acid solution is 100g/L.
上述一种利用L-抗坏血酸减弱低品位辉铜矿表面钝化效应的方法在低品位辉铜矿生物浸出方面的应用。The application of the method of using L-ascorbic acid to weaken the surface passivation effect of low-grade chalcocite ore in the bioleaching of low-grade chalcocite ore.
本发明的显著优点在于:Significant advantage of the present invention is:
本发明工艺流程短,操作简单,设备简单,能耗低,可以显著提高辉铜矿的生物浸出率,经测定,浸出20d后,Cu的浸出率最高可达96%。The invention has short technological process, simple operation, simple equipment and low energy consumption, and can significantly increase the bioleaching rate of chalcocite. It is determined that after 20 days of leaching, the Cu leaching rate can reach up to 96%.
附图说明Description of drawings
图1为本发明的工艺流程图。Fig. 1 is a process flow diagram of the present invention.
图2为本发明的pH测量值。Figure 2 shows the pH measurements of the present invention.
图3为本发明的Eh测量值。Fig. 3 is the measured value of Eh of the present invention.
图4为本发明的铜浸出率图。Fig. 4 is the graph of copper leaching rate of the present invention.
具体实施方式Detailed ways
为了使本发明所述的内容更加便于理解,下面结合具体实施方式对本发明所述的技术方案做进一步的说明,但是本发明不仅限于此。In order to make the content of the present invention easier to understand, the technical solutions of the present invention will be further described below in conjunction with specific embodiments, but the present invention is not limited thereto.
本发明中,所述9K培养基配方为:A液(g/L):3.0g/L(NH)2SO4、0.5g/L K2HPO4、0.1g/L KCl、0.5g/L MgSO4·7H2O、0.01g/L Ca(NO3)2、去离子水800mL,调节pH值至2.0,121℃高压灭菌20min;B液:FeSO4·7H2O 44.3g/L、去离子水200mL,调节pH值至2.0,0.22μm滤膜过滤除菌;将灭菌后的800mLA液与200mLB液混匀后分装。In the present invention, the formula of the 9K medium is: Liquid A (g/L): 3.0g/L (NH) 2 SO 4 , 0.5g/L K 2 HPO 4 , 0.1g/L KCl, 0.5g/L MgSO 4 7H 2 O, 0.01g/L Ca(NO 3 ) 2 , 800mL deionized water, adjust the pH value to 2.0, autoclave at 121°C for 20min; liquid B: FeSO 4 7H 2 O 44.3g/L, deionized 200mL of ionized water, adjust the pH value to 2.0, filter and sterilize with a 0.22μm membrane filter; mix 800mL of the sterilized A solution and 200mL of the B solution, and dispense.
本发明中,所述无铁9K培养基的配方为:3.0g/L(NH)2SO4、0.5g/L K2HPO4、0.1g/LKCl、0.5g/L MgSO4·7H2O、0.01g/L Ca(NO3)2、去离子水1000mL,调节pH值至2.0,121℃高压灭菌20min。In the present invention, the formulation of the iron-free 9K medium is: 3.0g/L (NH) 2 SO 4 , 0.5g/LK 2 HPO 4 , 0.1g/LKCl, 0.5g/L MgSO 4 ·7H 2 O, 0.01g/L Ca(NO 3 ) 2 , 1000mL deionized water, adjust the pH value to 2.0, and autoclave at 121°C for 20min.
本发明中,所述低品位辉铜矿的多元素分析结果及铜化学物相分析结果如表1和表2所列。In the present invention, the multi-element analysis results and copper chemical phase analysis results of the low-grade chalcocite are listed in Table 1 and Table 2.
表1低品位辉铜矿的多元素分析结果(%)Table 1 The multi-element analysis results (%) of low-grade chalcocite
表2低品位辉铜矿的铜化学物相分析结果(%)The copper chemical phase analysis result (%) of table 2 low-grade chalcocite
本发明中,所述辉铜矿纯矿物的多元素分析结果如表3所列。In the present invention, the multi-element analysis results of the chalcocite pure mineral are listed in Table 3.
表3辉铜矿纯矿物的多元素分析结果Table 3 Multi-element analysis results of chalcocite pure minerals
本发明中,对所述嗜酸性氧化亚铁硫杆菌、氧化亚铁钩端螺旋菌、嗜酸性铁原体菌三种铁细菌的来源没有特殊限制,采用本领域所熟知的铁细菌的来源即可,具体的,本发明实施例当中的三种铁细菌分离自福建省龙岩市紫金山硫化矿山的酸性硐坑水。In the present invention, there is no special limitation on the sources of the three kinds of iron bacteria, acidophilic Thiobacillus ferrooxidans, Leptospira ferrooxidans, and acidophilic ferroplasma, and the source of iron bacteria known in the art is Yes, specifically, the three iron bacteria in the examples of the present invention were isolated from the acid pit water of the Zijinshan sulfide mine in Longyan City, Fujian Province.
本发明中,pH值测定采用奥豪斯ST3100型酸度计,Eh值测定采用METTLER TOLEDO电位计,铜铁含量测定采用iCAP7400电感耦合等离子体发射光谱仪。In the present invention, Ohaus ST3100 acidity meter is used for pH value measurement, METTLER TOLEDO potentiometer is used for Eh value measurement, and iCAP7400 inductively coupled plasma emission spectrometer is used for copper and iron content measurement.
试验组1Test group 1
一种减弱低品位辉铜矿表面钝化效应的方法,按如下步骤进行:A method for weakening the surface passivation effect of low-grade chalcocite, carried out as follows:
(1)将低品位辉铜矿经过破碎、磨矿、分级等操作,制为粒度≤74μm的粉末,对制得的具有代表性的样品进行定量分析检测,Cu品位为0.30%;(1) Process low-grade chalcocite through operations such as crushing, ore grinding, and grading to produce powders with a particle size of ≤74 μm, and carry out quantitative analysis and detection on the representative samples obtained, and the Cu grade is 0.30%;
(2)将10mL铁细菌混合菌液接入90mL 9K培养基,用50%(v/v)硫酸溶液调节pH值为1.8,放置在30℃、150r/min恒温振荡培养箱振荡培养,每6d按10vol%接种量传代一次,当培养液颜色由淡绿色变为红棕色时结束传代,得到传代培养菌液;所述铁细菌混合菌液由1×107CFU/mL嗜酸性氧化亚铁硫杆菌、1×106CFU/mL氧化亚铁钩端螺旋菌及1×104CFU/mL嗜酸性铁原体菌组成;(2) Put 10mL iron bacteria mixed bacteria solution into 90mL 9K medium, adjust the pH value to 1.8 with 50% (v/v) sulfuric acid solution, place in 30°C, 150r/min constant temperature shaking incubator for shaking culture, every 6d Passage once according to the inoculum amount of 10vol%, and end the passage when the color of the culture solution changes from light green to reddish brown, and obtain the subculture bacterial liquid; the mixed bacterial liquid of iron bacteria is composed of 1×10 7 CFU/mL Bacillus, 1×10 6 CFU/mL Leptospira ferrous oxide and 1×10 4 CFU/mL acidophilic ferroplasma;
(3)取10mL步骤(2)得到的传代培养菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到一次驯化菌液;取10mL一次驯化菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到二次驯化菌液;经测定,二次驯化菌液中含有嗜酸性氧化亚铁硫杆菌1×108CFU/mL、氧化亚铁钩端螺旋菌1×107CFU/mL、嗜酸性铁原体菌1×105CFU/mL;(3) Take 10 mL of the subculture culture solution obtained in step (2) and put it in a 250 mL Erlenmeyer flask, put it into a constant temperature shaking incubator at a temperature of 30 °C and 150 r/min for shaking culture, and add 90 mL of no Iron 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6 days until the culture medium turns reddish brown, and obtain a primary domesticated bacterial liquid; take 10mL primary domesticated bacterial liquid and place it in a 250mL Erlenmeyer flask at a temperature of 30°C , 150r/min constant temperature shaking incubator shaking culture, when the bacteria grow to the logarithmic phase, add 90mL iron-free 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6d until the culture medium turns reddish brown, and obtain the secondary Acclimatized bacteria liquid; the secondary domesticated bacteria liquid contains 1×10 8 CFU/mL of acidophilic Thiobacillus ferrooxidans, 1×10 7 CFU/mL of Leptospira ferrooxidans, and acidophilic ferroplasma 1×10 5 CFU/mL;
(4)在250mL锥形瓶中加入2~3g步骤(1)得到的低品位辉铜矿样粉末、10mL步骤(3)得到的二次驯化菌液、90mL无铁9K培养基,置于温度40±5℃、180±10r/min恒温振荡培养箱中进行生物揺瓶浸出,实时监控浸出体系的pH值和Eh值,整个浸出周期为20d;(4) In a 250mL Erlenmeyer flask, add 2 to 3g of the low-grade chalcocite sample powder obtained in step (1), 10mL of the secondary domesticated bacteria liquid obtained in step (3), and 90mL of iron-free 9K medium, and place at temperature 40±5°C, 180±10r/min constant temperature shaking incubator for bio-bottle leaching, real-time monitoring of the pH value and Eh value of the leaching system, and the entire leaching cycle is 20d;
(6)浸出结束后,将浸出体系进行固液分离,得到浸出液和浸出残渣,进行ICP检测,经过计算,Cu浸出率为66%。(6) After the leaching is completed, the leaching system is subjected to solid-liquid separation to obtain the leaching solution and leaching residue, which are tested by ICP. After calculation, the leaching rate of Cu is 66%.
试验组2Test group 2
一种减弱低品位辉铜矿表面钝化效应的方法,按如下步骤进行:A method for weakening the surface passivation effect of low-grade chalcocite, carried out as follows:
(1)将低品位辉铜矿经过破碎、磨矿、分级等操作,制得粒度≤74μm的粉末,对制得的具有代表性的样品进行定量分析检测,Cu品位为0.30%;(1) The low-grade chalcocite is subjected to operations such as crushing, ore grinding, and grading to obtain a powder with a particle size of ≤74 μm, and quantitative analysis is performed on the representative sample obtained, and the Cu grade is 0.30%;
(2)将10mL铁细菌混合菌液接入90mL 9K培养基,用50%(v/v)硫酸溶液调节pH值为1.8,放置在30℃、150r/min恒温振荡培养箱振荡培养,每6d按10vol%接种量传代一次,当培养液颜色由淡绿色变为红棕色时结束传代,得到传代培养菌液;所述铁细菌混合菌液由1×107CFU/mL嗜酸性氧化亚铁硫杆菌、1×106CFU/mL氧化亚铁钩端螺旋菌及1×104CFU/mL嗜酸性铁原体菌组成;(2) Put 10mL iron bacteria mixed bacteria solution into 90mL 9K medium, adjust the pH value to 1.8 with 50% (v/v) sulfuric acid solution, place in 30°C, 150r/min constant temperature shaking incubator for shaking culture, every 6d Passage once according to the inoculum amount of 10vol%, and end the passage when the color of the culture solution changes from light green to reddish brown, and obtain the subculture bacterial liquid; the mixed bacterial liquid of iron bacteria is composed of 1×10 7 CFU/mL Bacillus, 1×10 6 CFU/mL Leptospira ferrous oxide and 1×10 4 CFU/mL acidophilic ferroplasma;
(3)取10mL步骤(2)得到的传代培养菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到一次驯化菌液;取10mL一次驯化菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到二次驯化菌液;经测定,二次驯化菌液中含有嗜酸性氧化亚铁硫杆菌1×108CFU/mL、氧化亚铁钩端螺旋菌1×107CFU/mL、嗜酸性铁原体菌1×105CFU/mL。(3) Take 10 mL of the subculture culture solution obtained in step (2) and put it in a 250 mL Erlenmeyer flask, put it into a constant temperature shaking incubator at a temperature of 30 °C and 150 r/min for shaking culture, and add 90 mL of no Iron 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6 days until the culture medium turns reddish brown, and obtain a primary domesticated bacterial liquid; take 10mL primary domesticated bacterial liquid and place it in a 250mL Erlenmeyer flask at a temperature of 30°C , 150r/min constant temperature shaking incubator shaking culture, when the bacteria grow to the logarithmic phase, add 90mL iron-free 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6d until the culture medium turns reddish brown, and obtain the secondary Acclimatized bacteria liquid; the secondary domesticated bacteria liquid contains 1×10 8 CFU/mL of acidophilic Thiobacillus ferrooxidans, 1×10 7 CFU/mL of Leptospira ferrooxidans, and acidophilic ferroplasma 1×10 5 CFU/mL.
(4)在250mL锥形瓶中加入2~3g步骤(1)得到的低品位辉铜矿样粉末、10mL步骤(3)得到的二次驯化菌液、90mL无铁9K培养基,置于温度40±5℃、180±10r/min恒温振荡培养箱中进行生物揺瓶浸出,实时监控浸出体系的pH值和Eh值,整个浸出周期为20d;在浸出过程中对浸出体系的pH值和Eh值进行监控,每间隔24h测量一次;每次测量后,当浸出体系的pH测量值超过1.90±0.05时,用50%(v/v)的硫酸进行调控使pH值控制在1.90±0.05。(4) In a 250mL Erlenmeyer flask, add 2 to 3g of the low-grade chalcocite sample powder obtained in step (1), 10mL of the secondary domesticated bacteria liquid obtained in step (3), and 90mL of iron-free 9K medium, and place at temperature 40±5°C, 180±10r/min constant temperature shaking incubator for biological bottle leaching, real-time monitoring of the pH value and Eh value of the leaching system, the whole leaching cycle is 20d; during the leaching process, the pH value and Eh value of the leaching system The value is monitored and measured every 24 hours; after each measurement, when the pH measurement value of the leaching system exceeds 1.90±0.05, the pH value is controlled at 1.90±0.05 with 50% (v/v) sulfuric acid.
(5)浸出结束后,将浸出体系进行固液分离,得到浸出液和浸出残渣,进行ICP检测,经过计算,Cu浸出率为75%。(5) After the leaching is completed, the leaching system is subjected to solid-liquid separation to obtain leaching liquid and leaching residue, and ICP detection is carried out. After calculation, the leaching rate of Cu is 75%.
试验组3Test group 3
一种利用L-抗坏血酸减弱低品位辉铜矿表面钝化效应的方法,按如下步骤进行:A method utilizing L-ascorbic acid to weaken the surface passivation effect of low-grade chalcocite, carried out as follows:
(1)将低品位辉铜矿经过破碎、磨矿、分级等操作,制得粒度≤74μm的粉末,对制得的具有代表性的样品进行定量分析检测,Cu品位为0.30%。(1) The low-grade chalcocite is subjected to crushing, grinding, grading and other operations to obtain a powder with a particle size of ≤74 μm. Quantitative analysis and detection is carried out on the representative sample obtained, and the Cu grade is 0.30%.
(2)将10mL铁细菌混合菌液接入90mL 9K培养基,用50%(v/v)硫酸溶液调节pH值为1.8,放置在30℃、150r/min恒温振荡培养箱振荡培养,每6d按10vol%接种量传代一次,当培养液颜色由淡绿色变为红棕色时结束传代,得到传代培养菌液;所述铁细菌混合菌液由1×107CFU/mL嗜酸性氧化亚铁硫杆菌、1×106CFU/mL氧化亚铁钩端螺旋菌及1×104CFU/mL嗜酸性铁原体菌组成;(2) Put 10mL iron bacteria mixed bacteria solution into 90mL 9K medium, adjust the pH value to 1.8 with 50% (v/v) sulfuric acid solution, place in 30°C, 150r/min constant temperature shaking incubator for shaking culture, every 6d Passage once according to the inoculum amount of 10vol%, and end the passage when the color of the culture solution changes from light green to reddish brown, and obtain the subculture bacterial liquid; the mixed bacterial liquid of iron bacteria is composed of 1×10 7 CFU/mL Bacillus, 1×10 6 CFU/mL Leptospira ferrous oxide and 1×10 4 CFU/mL acidophilic ferroplasma;
(3)取10mL步骤(2)得到的传代培养菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到一次驯化菌液;取10mL一次驯化菌液置于250mL锥形瓶中,放入温度30℃、150r/min恒温振荡培养箱振荡培养,待细菌生长至对数期时加入90mL无铁9K培养基和1.0g辉铜矿纯矿物,继续培养约6d直至培养液变为红棕色,得到二次驯化菌液;经测定,二次驯化菌液中含有嗜酸性氧化亚铁硫杆菌1×108CFU/mL、氧化亚铁钩端螺旋菌1×107CFU/mL、嗜酸性铁原体菌1×105CFU/mL。(3) Take 10 mL of the subculture culture solution obtained in step (2) and put it in a 250 mL Erlenmeyer flask, put it into a constant temperature shaking incubator at a temperature of 30 °C and 150 r/min for shaking culture, and add 90 mL of no Iron 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6 days until the culture medium turns reddish brown, and obtain a primary domesticated bacterial liquid; take 10mL primary domesticated bacterial liquid and place it in a 250mL Erlenmeyer flask at a temperature of 30°C , 150r/min constant temperature shaking incubator shaking culture, when the bacteria grow to the logarithmic phase, add 90mL iron-free 9K medium and 1.0g chalcocite pure mineral, continue to cultivate for about 6d until the culture medium turns reddish brown, and obtain the secondary Acclimatized bacteria liquid; the secondary domesticated bacteria liquid contains 1×10 8 CFU/mL of acidophilic Thiobacillus ferrooxidans, 1×10 7 CFU/mL of Leptospira ferrooxidans, and acidophilic ferroplasma 1×10 5 CFU/mL.
(4)在250mL锥形瓶中加入2~3g步骤(1)得到的低品位辉铜矿粉末、10mL步骤(3)得到的二次驯化菌液和90mL无铁9K培养基,置于温度40±5℃、180±10r/min的恒温振荡培养箱中进行生物揺瓶浸出,整个浸出周期为20d,在浸出过程中对浸出体系的pH值和Eh值进行监控,每间隔24h测量一次;每次测量后,当浸出体系的pH测量值超过1.90±0.05时用50%(v/v)的硫酸溶液降低pH值至1.90±0.05,当浸出体系的Eh值超过500±5mV时用100g/L的L-抗坏血酸溶液降低Eh值至500±5mV。(4) In a 250mL Erlenmeyer flask, add 2-3g of the low-grade chalcocite powder obtained in step (1), 10mL of the secondary domesticated bacteria liquid obtained in step (3) and 90mL of iron-free 9K medium, and place at a temperature of 40 Biological bottle leaching is carried out in a constant temperature shaking incubator at ±5°C and 180±10r/min. The entire leaching cycle is 20 days. During the leaching process, the pH value and Eh value of the leaching system are monitored and measured every 24 hours; After the first measurement, use 50% (v/v) sulfuric acid solution to reduce the pH value to 1.90±0.05 when the pH measurement value of the leaching system exceeds 1.90±0.05, and use 100g/L when the Eh value of the leaching system exceeds 500±5mV The L-ascorbic acid solution reduces the Eh value to 500±5mV.
(5)浸出结束后,将浸出体系进行固液分离,得到浸出液和浸出残渣,进行ICP检测,经过计算,Cu浸出率为96%。(5) After the leaching is completed, the leaching system is subjected to solid-liquid separation to obtain leaching liquid and leaching residue, and ICP detection is performed. After calculation, the leaching rate of Cu is 96%.
以上所述仅为本发明的较佳实施例,凡依本发明申请专利范围所做的均等变化与修饰,皆应属本发明的涵盖范围。The above descriptions are only preferred embodiments of the present invention, and all equivalent changes and modifications made according to the scope of the patent application of the present invention shall fall within the scope of the present invention.
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Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20070042482A1 (en) * | 2005-08-17 | 2007-02-22 | Biosigma S.A. | Sulfur-oxidizing bacteria and their use in bioleaching processes for sulfured copper minerals |
| CN101191153A (en) * | 2006-11-28 | 2008-06-04 | 北京有色金属研究总院 | Pyrite selectivity inhibition technique for secondary copper sulfide mineral biological lixiviation process |
| CN109680153A (en) * | 2019-01-28 | 2019-04-26 | 东北大学 | The method for improving metal Bioleaching rate in abandoned printed circuit board using graphite |
-
2023
- 2023-05-29 CN CN202310611776.6A patent/CN116640925A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20070042482A1 (en) * | 2005-08-17 | 2007-02-22 | Biosigma S.A. | Sulfur-oxidizing bacteria and their use in bioleaching processes for sulfured copper minerals |
| CN101191153A (en) * | 2006-11-28 | 2008-06-04 | 北京有色金属研究总院 | Pyrite selectivity inhibition technique for secondary copper sulfide mineral biological lixiviation process |
| CN109680153A (en) * | 2019-01-28 | 2019-04-26 | 东北大学 | The method for improving metal Bioleaching rate in abandoned printed circuit board using graphite |
Non-Patent Citations (4)
| Title |
|---|
| 何进祥等: "《环境微生物学》", 30 April 2018, 电子科技大学出版社, pages: 185 - 186 * |
| 余靖冉等: "低品位铜矿浸出菌的筛选", 化工管理, no. 19, 1 July 2018 (2018-07-01), pages 43 - 44 * |
| 武彪等: "辉铜矿单矿物的氧化行为研究", 有色金属, no. 03, 15 August 2008 (2008-08-15), pages 58 - 61 * |
| 赖晓康: "紫金山低品位铜矿生物浸出第二阶段主要影响因素研究", 福建冶金, no. 04, 7 July 2021 (2021-07-07), pages 12 - 16 * |
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