The grown conditions of Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans were investigated,and then experiments were conducted to research the bioleaching behaviors of crude ore of copper sulfide and h...The grown conditions of Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans were investigated,and then experiments were conducted to research the bioleaching behaviors of crude ore of copper sulfide and hand-picked concentrates of chalcopyrite by Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans.The experimental results show that the bacteria grow best when the temperature is(30±1) °C and the pH value is 2.0.The bacteria concentration is 2.24×107 mL-1 in this condition.It is found that the copper extraction yield is affected by the inoculum size and the pulp density and the extraction yield increases as the inoculum size grows.The bioleaching rates reach their highest point in sulfide copper and chalcopyrite with a pulp density of 5% and 10%,respectively.Column flotation experiments of low-grade copper sulfide ores show that the bioleaching recovery reaches nearly 45% after 75 days.展开更多
Bacterial leaching of single sulfide minerals and polymetallic sulfide ores was operated in shake flasks and small-scaled columns.The results show that bioleaching of jamesonite is not accessible,the iron extraction r...Bacterial leaching of single sulfide minerals and polymetallic sulfide ores was operated in shake flasks and small-scaled columns.The results show that bioleaching of jamesonite is not accessible,the iron extraction rate of pyrrhotite bioleaching reaches 98.2% after 26 d,and the zinc extraction rate of marmatite bioleaching reaches 92.3%,while the corresponding iron extraction reaches only 13.6% after 29 d.Pulp density has a significant effect on metal extraction of pyrrhotite and marmatite bioleaching.The corresponding metal extraction rate decreases with the increase of pulp density.For the polymetallic sulfide ores,zinc extraction of 97.1% is achieved after bioleaching in shake flasks for 10 d,while only 7.8% is obtained after bioleaching in small-scaled column.Analytical results of scanning electron microscopy(SEM) and energy dispersive X-ray analysis(EDX) reveal that large amount of calcium sulfate is formed on the mineral surface.展开更多
The bioleaching of chalcopyrite is low cost and environmentally friendly,but the leaching rate is low.To explore the mechanism of chalcopyrite bioleaching and improve its leaching rate,the effect and mechanism of mang...The bioleaching of chalcopyrite is low cost and environmentally friendly,but the leaching rate is low.To explore the mechanism of chalcopyrite bioleaching and improve its leaching rate,the effect and mechanism of manganese ions(Mn^(2+))and visible light on chalcopyrite mediated by Acidithiobacillus ferrooxidans(A.ferrooxidans)were discussed.Bioleaching experiments showed that when both Mn^(2+)and visible light were present,the copper extraction was 14.38%higher than that of the control system(without Mn^(2+)and visible light).Moreover,visible light and Mn^(2+)promoted the growth of A.ferrooxidans.Scanning electron microscopy(SEM)and energy dispersive spectrometer(EDS)analysis revealed that Mn^(2+)promoted the formation of extracellular polymeric substance(EPS)on the surface of chalcopyrite,changed the morphology of A.ferrooxidans,enhanced the adsorption of bacteria on chalcopyrite surface with light illumination,and thus promoted the bioleaching of chalcopyrite.UV–vis absorbance spectra indicated that Mn^(2+)promoted the response of chalcopyrite to visible light and enhanced the catalytic effect of visible light on chalcopyrite bioleaching.Based on X-ray photoelectron spectroscopy(XPS),the relevant sulfur speciation of chalcopyrite before and after bioleaching were analyzed and the results revealed that visible light and Mn^(2+)promoted chalcopyrite bioleaching by reducing the formation of passivation layer(S_(n)^(2-)/S0).Investigation into electrochemical results further indicated that Mn^(2+)and visible light improved the electrochemical activity of chalcopyrite,thus increasing the bioleaching rate.展开更多
银能有效地催化黄铜矿浸出,本文使用含银固体废弃物作为催化剂,研究了不同黄铜矿/含银固体废弃物配比下的浸出动力学行为。体系的生物浸出行为表明,含银固体废弃物能有效催化浸出黄铜矿。固体废弃物的加入使得体系的氧化还原电位远高于...银能有效地催化黄铜矿浸出,本文使用含银固体废弃物作为催化剂,研究了不同黄铜矿/含银固体废弃物配比下的浸出动力学行为。体系的生物浸出行为表明,含银固体废弃物能有效催化浸出黄铜矿。固体废弃物的加入使得体系的氧化还原电位远高于其他学者所提出的最适电位区间(380~480 mV vs Ag/AgCl),体系浸出温度与铜浸出率呈正相关性。在此浸出条件下,黄铜矿的生物浸出主要由扩散控制,表面活化能Ea为28.24 kJ/mol。本工作对推广微生物作用下银催化黄铜矿浸出的工业应用有参考价值。展开更多
基金Project(2012AA061501)supported by the National High-tech Research and Development Program of ChinaProject(20120162120010)supported by the Research Fund for the Doctoral Program of Higher Education of China+2 种基金Project(NCET-13-0595)supported by the program for New Century Excellent Talents in University of ChinaProject(51374248)supported by the National Natural Science Foundation of ChinaProject(2010CB630905)supported by the National Key Basic Research Program of China
文摘The grown conditions of Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans were investigated,and then experiments were conducted to research the bioleaching behaviors of crude ore of copper sulfide and hand-picked concentrates of chalcopyrite by Acidithiobacillus ferrooxidans and Acidithiobacillus thiooxidans.The experimental results show that the bacteria grow best when the temperature is(30±1) °C and the pH value is 2.0.The bacteria concentration is 2.24×107 mL-1 in this condition.It is found that the copper extraction yield is affected by the inoculum size and the pulp density and the extraction yield increases as the inoculum size grows.The bioleaching rates reach their highest point in sulfide copper and chalcopyrite with a pulp density of 5% and 10%,respectively.Column flotation experiments of low-grade copper sulfide ores show that the bioleaching recovery reaches nearly 45% after 75 days.
基金Project(51374248) supported by the National Natural Science Foundation of ChinaProject(NCET-13-0595) supported by Program for New Century Excellent Talents in University,China+1 种基金Project(2012AA061501) supported by the National High Technology Research and Development Program of ChinaProject(20120162120010) supported by the Research Fund for the Doctoral Program of Higher Education of China
文摘Bacterial leaching of single sulfide minerals and polymetallic sulfide ores was operated in shake flasks and small-scaled columns.The results show that bioleaching of jamesonite is not accessible,the iron extraction rate of pyrrhotite bioleaching reaches 98.2% after 26 d,and the zinc extraction rate of marmatite bioleaching reaches 92.3%,while the corresponding iron extraction reaches only 13.6% after 29 d.Pulp density has a significant effect on metal extraction of pyrrhotite and marmatite bioleaching.The corresponding metal extraction rate decreases with the increase of pulp density.For the polymetallic sulfide ores,zinc extraction of 97.1% is achieved after bioleaching in shake flasks for 10 d,while only 7.8% is obtained after bioleaching in small-scaled column.Analytical results of scanning electron microscopy(SEM) and energy dispersive X-ray analysis(EDX) reveal that large amount of calcium sulfate is formed on the mineral surface.
基金supported by the National Natural Science Foun-dation of China(51774332,51934009,U1932129)Fundamental Research Funds for the Central Universities of Central South University(2021zzts0299)the college students innovations special project funded by Hunan province(S2021105330471).
文摘The bioleaching of chalcopyrite is low cost and environmentally friendly,but the leaching rate is low.To explore the mechanism of chalcopyrite bioleaching and improve its leaching rate,the effect and mechanism of manganese ions(Mn^(2+))and visible light on chalcopyrite mediated by Acidithiobacillus ferrooxidans(A.ferrooxidans)were discussed.Bioleaching experiments showed that when both Mn^(2+)and visible light were present,the copper extraction was 14.38%higher than that of the control system(without Mn^(2+)and visible light).Moreover,visible light and Mn^(2+)promoted the growth of A.ferrooxidans.Scanning electron microscopy(SEM)and energy dispersive spectrometer(EDS)analysis revealed that Mn^(2+)promoted the formation of extracellular polymeric substance(EPS)on the surface of chalcopyrite,changed the morphology of A.ferrooxidans,enhanced the adsorption of bacteria on chalcopyrite surface with light illumination,and thus promoted the bioleaching of chalcopyrite.UV–vis absorbance spectra indicated that Mn^(2+)promoted the response of chalcopyrite to visible light and enhanced the catalytic effect of visible light on chalcopyrite bioleaching.Based on X-ray photoelectron spectroscopy(XPS),the relevant sulfur speciation of chalcopyrite before and after bioleaching were analyzed and the results revealed that visible light and Mn^(2+)promoted chalcopyrite bioleaching by reducing the formation of passivation layer(S_(n)^(2-)/S0).Investigation into electrochemical results further indicated that Mn^(2+)and visible light improved the electrochemical activity of chalcopyrite,thus increasing the bioleaching rate.
基金Project(2018JJ1041)supported by the Natural Science Foundation of Hunan,ChinaProjects(51774332,U1932129,51804350 and 51934009)supported by the National Natural Science Foundation of China。
文摘银能有效地催化黄铜矿浸出,本文使用含银固体废弃物作为催化剂,研究了不同黄铜矿/含银固体废弃物配比下的浸出动力学行为。体系的生物浸出行为表明,含银固体废弃物能有效催化浸出黄铜矿。固体废弃物的加入使得体系的氧化还原电位远高于其他学者所提出的最适电位区间(380~480 mV vs Ag/AgCl),体系浸出温度与铜浸出率呈正相关性。在此浸出条件下,黄铜矿的生物浸出主要由扩散控制,表面活化能Ea为28.24 kJ/mol。本工作对推广微生物作用下银催化黄铜矿浸出的工业应用有参考价值。
基金Project(207154)supported by the Postdoctoral Research Funding of Central South University,ChinaProjects(31470230,51320105006,51604308)supported by the National Natural Science Foundation of China+2 种基金Project(2017RS3003)supported by the Youth Talent Foundation of Hunan Province,ChinaProject(2018JJ2486)supported by the Natural Science Foundation of Hunan Province,ChinaProject(2018WK2012)supported by the Key Research and Development Projects in Hunan Province,China。
基金Projects(31470230,51320105006,51604308)supported by the National Natural Science Foundation of ChinaProject(2017RS3003)supported by the Youth Talent Foundation of Hunan Province of China+1 种基金Project(2018JJ2486)supported by the Natural Science Foundation of Hunan Province of ChinaProject(2018WK2012)supported by the Key Research and Development Projects in Hunan Province,China。
基金Projects(31470230,51320105006,51604308)supported by the National Natural Science Foundation of ChinaProject(2017RS3003)supported by the Youth Talent Foundation of Hunan Province of China+2 种基金Project(2018JJ2486)supported by the Natural Science Foundation of Hunan Province of ChinaProject(2018WK2012)supported by the Key Research and Development Projects in Hunan Province,ChinaProject(2018zzts767)supported by the Fundamental Research Funds for the Central Universities,China。
基金Project(2018JJ1041)supported by the Natural Science Foundation of Hunan,ChinaProjects(51774332,51934009,U1932129)supported by the National Natural Science Foundation of China。
基金Projects(51774332,U1932129,51804350,51934009)supported by the National Natural Science Foundation of ChinaProject(2018JJ1041)supported by the Natural Science Foundation of Hunan Province,China。
基金Projects(51604308,41771300,41301274)supported by the National Natural Science Foundation of ChinaProject(2017QNCXTD_GTD)supported by the Youth Innovation Team Project of Institute of Subtropical Agriculture,Chinese Academy of Sciences+1 种基金Project(2017YFD0202000)supported by the National Key Research and Development Program of ChinaProject(2020GDASYL-20200402001)supported by the special Project of Science and Technology Development,China。