Ma Yingqun, Lin Chuxia
Centre for Ecological and Environmental Technologies, South China Agricultural University, Guangzhou 510642, China.
Sci Rep. 2013;3:1979. doi: 10.1038/srep01979.
At an initial pH of 2, while abiotic oxidation of aqueous Fe(2+) was enhanced by a flux of H2O2 at micromolar concentrations, bio-oxidation of aqueous Fe(2+) could be impeded due to oxidative stress/damage in Acidithiobacillus ferrooxidans caused by Fenton reaction-derived hydroxyl radical, particularly when the molar ratio of Fe(2+) to H2O2 was low. When pyrite cubes were intermittently exposed to fluxes of micromolar H2O2, the reduced Fe(2+)-Fe(3+) conversion rate in the solution (due to reduced microbial activity) weakened the Fe(3+)-catalyzed oxidation of cubic pyrite and added to relative importance of H2O2-driven oxidation in the corrosion of mineral surfaces for the treatments with high H2O2 doses. This had effects on reducing the build-up of a passivating coating layer on the mineral surfaces. Cell attachment to the mineral surfaces was only observed at the later stage of the experiment after the solutions became less favorable for the growth of planktonic bacteria.
在初始pH值为2时,虽然微摩尔浓度的过氧化氢通量会增强水溶液中Fe(Ⅱ)的非生物氧化,但由于芬顿反应产生的羟基自由基对嗜酸氧化亚铁硫杆菌造成氧化应激/损伤,水溶液中Fe(Ⅱ)的生物氧化可能会受到阻碍,尤其是当Fe(Ⅱ)与过氧化氢的摩尔比很低时。当黄铁矿立方体间歇性地暴露于微摩尔浓度的过氧化氢通量下时,溶液中Fe(Ⅱ)-Fe(Ⅲ)转化率降低(由于微生物活性降低),削弱了Fe(Ⅲ)催化的立方黄铁矿氧化,并增加了高剂量过氧化氢处理下过氧化氢驱动的氧化在矿物表面腐蚀中的相对重要性。这对减少矿物表面钝化涂层的形成有影响。仅在实验后期,当溶液对浮游细菌的生长变得不利时,才观察到细胞附着在矿物表面。