North-Central Section - 50th Annual Meeting - 2016

Paper No. 2-5
Presentation Time: 9:20 AM

EFFECT OF MINERALOGY, PH, TEMPERATURE, SALINITY AND ANIONS ON THE ABILITY OF BACTERIA TO REDUCE FERRIC IRON OXIDES AND DRIVE DEEP SUBSURFACE DIAGENESIS


DONG, Yiran1, SANFORD, Robert A.2, BOYANOV, Maxim I.3, KEMNER, Kenneth M.3, FLYNN, Theodore M.3, O'LOUGHLIN, Edward J.3, GEORGE, Samantha4, FOUKE, Kaitlyn E.5 and FOUKE, Bruce W.6, (1)Carl R. Woese Institute for Genomic Biology, University of Illinois Urbana-Champaign, Urbana, IL 61801; Department of Geology, University of Illinois Urbana-Champaign, 1301 W. Green St, Urbana, IL 61801, (2)Department of Geology, University of Illinois Urbana-Champaign, 1301 W. Green St, Urbana, IL 61801, (3)Biosciences Division, Argonne National Laboratory, Argonne, IL 60439, (4)Department of Microbiology, University of Illinois Urbana-Champaign, Urbana, IL 61801, (5)Department of Biology, Denison University, Granville, OH 43023, (6)Department of Geology, University of Illinois Urbana-Champaign, 1301 W. Green St, Urbana, IL 61801; Carl R. Woese Institute for Genomic Biology, University of Illinois Urbana-Champaign, Urbana, IL 61801; Department of Microbiology, University of Illinois Urbana-Champaign, Urbana, IL 61801, dong5600@illinois.edu

Iron reduction by dissimilatory iron-reducing bacteria (DIRB), coupled with the oxidation of organic compounds or H2, causes formation of post-depositional (diagenetic) Fe(II)-containing minerals. Previous studies on the composition, distribution and precipitation rates of secondary minerals during microbial iron reduction have been primarily focused on ferrihydrite reduction by Shewanella spp. However, comparatively little is known about these processes by a variety of other DIRB and the effect of specific environmental factors on Fe(II)-bearing mineral diagenesis. Here we examine how environmental conditions influence the reduction of ferric iron minerals by Orenia metallireducens strain Z6, a DIRB from the phylum Firmicutes. This includes the effects of: (1) pH at 6.5-8.5; (2) temperature at 22-50 °C; (3) salinity at 2-20% NaCl; (4) solution chemistry of phosphate and sulfate; (5) electron shuttles (e.g., anthraquinone-2,6-disulfonate (AQDS)); and (6) the reactivity of a variety of iron oxides, including ferrihydrite, lepidocrocite, goethite, hematite, and magnetite. For a total of 19 culturing conditions, we measured ferrous iron produced over time using the ferrozine assay and formation of secondary minerals using scanning electron microscopy with energy-dispersive X-ray spectroscopy (SEM-EDS), X-Ray Diffraction (XRD), and extended X-ray absorption fine structure spectroscopy (Fe-edge XANES and EXAFS). Results show that both the rate and extent of DIRB reduction of ferrihydrite and lepidocrocite vastly exceeded those of the more crystalline minerals. SEM, XRD, Fe-edge XANES and EXAFS indicate diversity in the composition and relative abundance of Fe(II)-containing minerals such as, green rust, siderite, magnetite and/or vivianite under the different environmental conditions. However, the secondary mineralization products cannot be attributed to either the extent or kinetics of Fe(II). Instead, the precipitation and composition of these digenetic minerals have resulted from the intricate interplay of precipitation dynamics, adsorption of Fe(II) and subsequent transformation (dissolution and reprecipitation). This study establishes the first mechanistic understanding of the biomineralization during microbial iron reduction in a broad range of natural environments.