Although dissimilatory iron reducing bacteria (DIRB) are capable of reducin
g a number of metals in oxides and soluble forms, the factors controlling t
he rate/extent of magnetite reduction and the nature of the mineral product
s resulting from magnetite reduction are not well understood. This study wa
s carried out to investigate mechanisms and biogeochemical processes occurr
ing during magnetite reduction by the DIRE, Shewanella putrefaciens strains
CN32 and MR-1. Reduction experiments were pel formed with biogenic and syn
thetic magnetite in well-defined solutions. Biogenic magnetite was generate
d via microbial reduction of hydrous ferric oxide (HFO). Biogenic magnetite
in solutions buffered with either bicarbonate (HCO3-) or 1,4-piperazinedie
rhanesulfonic (PIPES), with or without P, was inoculated with strain CN32 a
nd provided with lactate as the electron donor. Synthetic magnetite in a ba
cteriological growth medium (M1) was inoculated with either aerobically or
anaerobically grown cells of strain (CN32 or MR-1). Fe(II) production was d
etermined by HCl extraction of bioreduced samples in comparison to uninocul
ated controls, and the resulting solids were characterized by X-ray diffrac
tion (XRD), Mossbauer spectroscopy, scanning and transmission electron micr
oscopy (SEM and TEM). The extent and rate of biogenic magnetite reduction i
n the bicarbonate-buffered medium was higher than that in the PIPES-buffere
d medium, via complexation of bioproduced Fe(II) with HCO3- (or PO43-) and
formation of siderite (vivianite). S, putrefaciens CN32 reduced more synthe
tic than biogenic magnetite with differences attributed mainly to medium co
mposition. In the HCO3--buffered solutions, Fe(III) in the biogenic magneti
te was reduced to Fe(II), and siderite precipitated. In the PIPES-buffered
medium, Fe(III) in biogenic magnetite was also reduced to Fe(II), but no se
condary mineral phases were observed. Vivianite formed in those solutions c
ontaining P and in all synthetic magnetite treatments where there was suffi
cient supply of P from the M1 medium. Electron microscopy and Mossbauer spe
ctroscopy results suggest that the reduction process involves dissolution-p
recipitation mechanisms as opposed to solid state conversion of magnetite t
o vivianite or siderite, The aqueous medium, pH, strain type, and bacterial
growth conditions all affected the extent of magnetite reduction. The abil
ity of DIRE to utilize Fe(III) in crystalline magnetite as an electron acce
ptor could have significant implications for biogeochemical processes in se
diments where Fe(III) in magnetite represents the largest pool of electron
acceptor. (C) 2000 Elsevier Science B.V. All rights reserved.