Photoreductive dissolution of colloidal iron oxides in natural waters

1984 ◽  
Vol 18 (11) ◽  
pp. 860-868 ◽  
Author(s):  
T. David. Waite ◽  
Francois M. M. Morel
1986 ◽  
Vol 112 (2) ◽  
pp. 412-420 ◽  
Author(s):  
T.David Waite ◽  
Alex Torikov ◽  
J.David Smith
Keyword(s):  

Author(s):  
Jean-Pierre Jolivet

Iron is Earth’s fourth most widespread element (6.2% in mass), behind oxygen, silicon, and aluminum. It exists mostly as ferric oxide and oxyhydroxide (Fig. 7.1a) and to a lesser extent as sulfide (pyrite), carbonate (siderite), and silicate (fayalite). Iron oxides are largely used in technological areas such as metallurgy, colored pigments, magnetic materials, and catalysts. They also play an important role in the environment because the dissolution of ferric oxides in natural waters, promoted by acid–base, redox, photochemical phenomena, and also microbial mediation, allows iron to be involved in many biogeochemical processes. Iron is present in many living organisms such as plants, bacteria, mollusks, animals, and humans in various forms: . . . Porphyrinic complexes of iron, which are active centers of hemoglobin and several ferredoxins involved in biological functions, especially respiration mechanism and photosynthesis. Nanoparticles of amorphous ferric oxyhydroxides in animal and human organisms as ferritin, which allows regulation and storage of iron and in various nanophases present in plants as phytoferritin. Crystalline iron oxy(hydroxi)des produced by biomineralization processes. Goethite, lepidocrocite, and magnetite are the main constituents of radulas and the teeth of mollusks (limpets, chitons). Magnetite nanoparticles produced by magnetotactic bacteria (Fig. 7.1b), as well as by bees and pigeons, are used for purposes of orientation and guiding along the lines of force of the Earth’s magnetic field. Green rusts are also ferric- ferrous compounds belonging to the biogeochemical cycle of iron. . . . The crystal chemistry of iron oxy(hydroxi)des is very rich. The ferric, ferrous, and mixed ferric- ferrous oxygenated compounds correspond to around a dozen crystal structural types (Fig. 7.2). Most of these crystal phases can be synthesized from solutions in the laboratory, giving rise to a most diversified chemistry. They are also formed in nature because of the large variability of physicochemical conditions: an acidity range from around pH 0 to 13; redox conditions from oxic to totally anoxic media; bacterial activity that can be extremely intense; salinity largely varying from almost pure waters to real brines; presence of many organic and inorganic ligands; and various photochemical processes.


1992 ◽  
Vol 25 (2) ◽  
pp. 207-216 ◽  
Author(s):  
S. Nakashima ◽  
M. Yagi

In order to clarify the mechanism of growth of musty-odor producing cyanobacteria, the effects of iron forms on growth and musty-odor production in four species of cyanobacteria, Oscillatoriabrevis, Anabaenamacrospora, Phormidiumtenue and Oscillatoriatenuis were studied using laboratory batch cultures. The former two cyanobacteria produce geosmin and the latter two produce 2-methylisoborneol (MIB). The growth of A. macrospora, P. tenue and O. tenuis was suppressed in the EDTA (chelating agent)-free CT medium. However, O. brevis grew well and produced geosmin in this medium as well as in the presence of EDTA. Thus, O. brevis showed an ability to utilize colloidal iron and even iron oxides for its growth. This suggests that O. brevis would be expected to produce a specific high affinity iron chelator (siderophore) in the chelator-free medium. In the presence of bathophenanthroline disulfonate (BPDS), a strong Fe(II) chelating agent, O. brevis and P. tenue were able to grow, but A. macrospora and O.tenuis did not. Furthermore, O.brevis was capable of growing in the medium containing a microbial siderophore, desferrioxamine B(DESF), instead of EDTA, but the other three cyanobacteria did not grow. These results show that O. brevis has an excellent ability to utilize a variety of iron forms including Fe (II I)-EDTA, Fe (II)-BPDS,.Fe (III)-DESF chelates, colloidal ferric hydroxide and more thermodynamically stable crystalline iron oxides (Fe2O3 and Fe3O4) in comparison with the other three musty-odor producing cyanobacteria isolated from Lake Biwa.


Langmuir ◽  
1990 ◽  
Vol 6 (3) ◽  
pp. 555-559 ◽  
Author(s):  
P. Mulvaney ◽  
V. Swayambunathan ◽  
F. Grieser ◽  
D. Meisel

1991 ◽  
Vol 40 (1-3) ◽  
pp. 133-142 ◽  
Author(s):  
Jacinta Enzweiler ◽  
Inés Joekes

2009 ◽  
Vol 76 (1) ◽  
pp. 184-189 ◽  
Author(s):  
Julian Bosch ◽  
Katja Heister ◽  
Thilo Hofmann ◽  
Rainer U. Meckenstock

ABSTRACT Microbial iron reduction is considered to be a significant subsurface process. The rate-limiting bioavailability of the insoluble iron oxyhydroxides, however, is a topic for debate. Surface area and mineral structure are recognized as crucial parameters for microbial reduction rates of bulk, macroaggregate iron minerals. However, a significant fraction of iron oxide minerals in the subsurface is supposed to be present as nanosized colloids. We therefore studied the role of colloidal iron oxides in microbial iron reduction. In batch growth experiments with Geobacter sulfurreducens, colloids of ferrihydrite (hydrodynamic diameter, 336 nm), hematite (123 nm), goethite (157 nm), and akaganeite (64 nm) were added as electron acceptors. The colloidal iron oxides were reduced up to 2 orders of magnitude more rapidly (up to 1,255 pmol h− 1 cell− 1) than bulk macroaggregates of the same iron phases (6 to 70 pmol h− 1 cell− 1). The increased reactivity was not only due to the large surface areas of the colloidal aggregates but also was due to a higher reactivity per unit surface. We hypothesize that this can be attributed to the high bioavailability of the nanosized aggregates and their colloidal suspension. Furthermore, a strong enhancement of reduction rates of bulk ferrihydrite was observed when nanosized ferrihydrite aggregates were added.


2002 ◽  
Vol 245 (1) ◽  
pp. 86-90 ◽  
Author(s):  
R.C. Plaza ◽  
J.L. Arias ◽  
M. Espín ◽  
M.L. Jiménez ◽  
A.V. Delgado

1996 ◽  
Vol 92 (5) ◽  
pp. 791-802 ◽  
Author(s):  
Colin Boxall ◽  
Geoff Kelsall ◽  
Zhao Zhang

Sign in / Sign up

Export Citation Format

Share Document