Coby Aaron J, Picardal Flynn W
Environmental Science Research Center, School of Public and Environmental Affairs, Indiana University, Bloomington, IN 47405, USA.
Appl Environ Microbiol. 2005 Sep;71(9):5267-74. doi: 10.1128/AEM.71.9.5267-5274.2005.
A recent study (D. C. Cooper, F. W. Picardal, A. Schimmelmann, and A. J. Coby, Appl. Environ. Microbiol. 69:3517-3525, 2003) has shown that NO(3)(-) and NO(2)(-) (NO(x)(-)) reduction by Shewanella putrefaciens 200 is inhibited in the presence of goethite. The hypothetical mechanism offered to explain this finding involved the formation of a Fe(III) (hydr)oxide coating on the cell via the surface-catalyzed, abiotic reaction between Fe(2+) and NO(2)(-). This coating could then inhibit reduction of NO(x)(-) by physically blocking transport into the cell. Although the data in the previous study were consistent with such an explanation, the hypothesis was largely speculative. In the current work, this hypothesis was tested and its environmental significance explored through a number of experiments. The inhibition of approximately 3 mM NO(3)(-) reduction was observed during reduction of a variety of Fe(III) (hydr)oxides, including goethite, hematite, and an iron-bearing, natural sediment. Inhibition of oxygen and fumarate reduction was observed following treatment of cells with Fe(2+) and NO(2)(-), demonstrating that utilization of other soluble electron acceptors could also be inhibited. Previous adsorption of Fe(2+) onto Paracoccus denitrificans inhibited NO(x)(-) reduction, showing that Fe(II) can reduce rates of soluble electron acceptor utilization by non-iron-reducing bacteria. NO(2)(-) was chemically reduced to N(2)O by goethite or cell-sorbed Fe(2+), but not at appreciable rates by aqueous Fe(2+). Transmission and scanning electron microscopy showed an electron-dense, Fe-enriched coating on cells treated with Fe(2+) and NO(2)(-). The formation and effects of such coatings underscore the complexity of the biogeochemical reactions that occur in the subsurface.
最近的一项研究(D. C. 库珀、F. W. 皮卡达尔、A. 施密尔曼和A. J. 科比,《应用与环境微生物学》69:3517 - 3525,2003年)表明,在针铁矿存在的情况下,腐败希瓦氏菌200对NO₃⁻和NO₂⁻(NOₓ⁻)的还原作用受到抑制。为解释这一发现所提出的假设机制涉及通过Fe²⁺与NO₂⁻之间的表面催化非生物反应在细胞表面形成Fe(III)(氢)氧化物涂层。然后这种涂层可以通过物理阻断向细胞内的转运来抑制NOₓ⁻的还原。尽管先前研究中的数据与这种解释一致,但该假设在很大程度上是推测性的。在当前的工作中,通过一系列实验对该假设进行了检验,并探讨了其环境意义。在还原包括针铁矿、赤铁矿和含铁天然沉积物在内的多种Fe(III)(氢)氧化物的过程中,观察到约3 mM NO₃⁻还原受到抑制。在用Fe²⁺和NO₂⁻处理细胞后,观察到氧气和富马酸还原受到抑制,这表明对其他可溶性电子受体的利用也可能受到抑制。先前Fe²⁺吸附到反硝化副球菌上会抑制NOₓ⁻还原,表明Fe(II)可以降低非铁还原细菌对可溶性电子受体的利用速率。NO₂⁻被针铁矿或细胞吸附的Fe²⁺化学还原为N₂O,但水溶液中的Fe²⁺还原速率不明显。透射电子显微镜和扫描电子显微镜显示,在用Fe²⁺和NO₂⁻处理的细胞上有电子致密、富含Fe的涂层。这种涂层的形成及其影响突出了地下发生的生物地球化学反应的复杂性。