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Acidithiobacillus ferrooxidans對軟錳礦浸出的影響

Effect of Acidithiobacillus ferrooxidans on pyrolusite bioleaching

  • 摘要: 利用循環伏安、交流阻抗譜和極化曲線研究了Acidithiobacillus ferrooxidans對軟錳礦在模擬浸出溶液(9K基礎培養基, A.ferrooxidans, Fe (Ⅲ), A.ferrooxidans+Fe (Ⅲ))中電化學腐蝕行為的影響; 利用模擬有菌/無菌浸出溶液中鈍化膜的Mott-Schottky理論比較了有無細菌存在情況下形成的鈍化膜的優劣性.結果表明, A.ferrooxidans促進MnO2/Mn2+氧化還原轉化, 催化MnO2/Mn (OH)2電極反應; 加速軟錳礦/溶液界面電子交換, 無鐵存在時A.ferrooxidans使電荷轉移內阻降低34%, 比含Fe (Ⅲ)無菌體系低11%;引起軟錳礦電極極化, 增強其氧化活性; 加速MnO2向MnO·OH轉化及其產物擴散.A.ferrooxidans與軟錳礦作用更傾向于間接作用機理.在選取的各模擬電解液(pH值為2.0)中, 0.2~0.4 V區間內軟錳礦形成耗盡層, 在模擬浸出溶液中形成的鈍化膜都表現出p-n-p-n型半導體性能.在選取的0.2 V極化電位下, 無鐵時引入A.ferrooxidans使膜中的施主/受主密度減少, 細菌含有多種基團參與半導體/溶液界面電子轉移反應, 接受界面間自由電子或填充空穴, 促使軟錳礦與溶液界面物質交換變頻繁; 含鐵溶液中加入A.ferrooxidans使得鈍化膜受主/施主密度增大, A.ferrooxidans降低了膜的耐腐蝕性, 因而促進軟錳礦浸出.

     

    Abstract: Biohydrometallurgy is an increasingly popular ore extraction technology and is especially applicable for low-grade ores. In particular, Acidithiobacillus ferrooxidans (A. ferrooxidans) is by far the most widely used bioleaching microorganism for leaching ores, including for sulfide ores and manganese dioxide ores. At present, many works are focused on the vital facilitating role of A. ferrooxidans in the cycles of sulfur and iron for sulfide ores bioleaching. However, research on the effect of A. ferrooxidans on manganese dioxide ores leaching is limited. The effects of A. ferrooxidans on the electrochemistry behavior of pyrolusite in simulated solutions (9K basic medium, A. ferrooxidans, Fe(Ⅲ), A. ferrooxidans+Fe(Ⅲ)) were investigated using cyclic voltammetry, electrochemical impedance spectroscopy (EIS), and potentiodynamic polarization. Mott-Schottky curves were utilized to determine the passive film formed on the surface of pyrolusite ore in the presence or absence of bacteria bath solutions. The results show that A. ferrooxidans promotes the redox of MnO2/Mn2+ and triggers the reaction of MnO2/Mn(OH)2. A. ferrooxidans accelerates electron exchange between pyrolusite and solution; in the A. ferrooxidans-simulated solution, the charge-transfer reaction resistance of manganese dioxide is 34% lower than that of the control (9K) and 11% lower than that of the Fe(Ⅲ) solution. Germs cause polarization of pyrolusite, leading to an increase in oxidative activity of manganese dioxide. Bacteria facilitate the transformation of MnO2 to MnO·OH and is beneficial to its diffusion. The indirect action mechanism is adopted to explain the interaction between A. ferrooxidans and pyrolusite. The passive films formed in simulated solutions exhibit p-n-p-n type semiconductor properties at the polarization potential of 0.2 V when pH is 2.0, and the depletion layer of pyrolusite appears between 0.2 and 0.4 V. Introducing A.ferrooxidans to the Fe(Ⅲ)-free solution decreases the donor density and the acceptor density because bacteria contain a variety of groups involved in electron transfer, which accept free electrons or fill holes, prompting the exchange of species between manganese oxide and solution. Admixing A. ferrooxidans to Fe(Ⅲ)-containing solution increases carrier density, reducing the corrosion resistance of membrane. The corrosion rate of pyrolusite increases with the addition of A. ferrooxidans.

     

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