Department of Civil and Environmental Engineering, The Pennsylvania State University, University Park, PA 16802-1408, USA.
Appl Environ Microbiol. 2011 Jan;77(2):545-54. doi: 10.1128/AEM.01550-10. Epub 2010 Nov 19.
Lower Red Eyes is an acid mine drainage site in Pennsylvania where low-pH Fe(II) oxidation has created a large, terraced iron mound downstream of an anoxic, acidic, metal-rich spring. Aqueous chemistry, mineral precipitates, microbial communities, and laboratory-based Fe(II) oxidation rates for this site were analyzed in the context of a depositional facies model. Depositional facies were defined as pools, terraces, or microterracettes based on cm-scale sediment morphology, irrespective of the distance downstream from the spring. The sediments were composed entirely of Fe precipitates and cemented organic matter. The Fe precipitates were identified as schwertmannite at all locations, regardless of facies. Microbial composition was studied with fluorescence in situ hybridization (FISH) and transitioned from a microaerophilic, Euglena-dominated community at the spring, to a Betaproteobacteria (primarily Ferrovum spp.)-dominated community at the upstream end of the iron mound, to a Gammaproteobacteria (primarily Acidithiobacillus)-dominated community at the downstream end of the iron mound. Microbial community structure was more strongly correlated with pH and geochemical conditions than depositional facies. Intact pieces of terrace and pool sediments from upstream and downstream locations were used in flowthrough laboratory reactors to measure the rate and extent of low-pH Fe(II) oxidation. No change in Fe(II) concentration was observed with (60)Co-irradiated sediments or with no-sediment controls, indicating that abiotic Fe(II) oxidation was negligible. Upstream sediments attained lower effluent Fe(II) concentrations compared to downstream sediments, regardless of depositional facies.
下红眼睛是宾夕法尼亚州的一个酸性矿山排水点,低 pH 值的 Fe(II)氧化作用在缺氧、酸性、富含金属的泉水下游形成了一个大型梯田状铁丘。在此背景下,对该地点的水化学、矿物沉淀、微生物群落和基于实验室的 Fe(II)氧化速率进行了分析。根据沉积相模型,沉积相被定义为根据 cm 级别的沉积物形态的水池、梯田或微梯田,而不管其距离泉水有多远。沉积物完全由 Fe 沉淀物和胶结有机质组成。所有位置的 Fe 沉淀物均鉴定为水羟铁矿,而与相无关。微生物组成通过荧光原位杂交(FISH)进行研究,并从泉水处的微需氧、裸藻为主的群落转变为上游铁丘末端的 Betaproteobacteria(主要是 Ferrovum spp.)为主的群落,再到下游铁丘末端的 Gammaproteobacteria(主要是 Acidithiobacillus)为主的群落。微生物群落结构与 pH 值和地球化学条件的相关性强于沉积相。使用来自上游和下游位置的完整的梯田和水池沉积物进行了流动实验室反应器实验,以测量低 pH 值 Fe(II)氧化的速率和程度。用 (60)Co 辐照的沉积物或无沉积物对照没有观察到 Fe(II)浓度的变化,表明非生物 Fe(II)氧化可以忽略不计。与下游沉积物相比,无论沉积相如何,上游沉积物的流出 Fe(II)浓度都较低。