Abstract:
Salt pond is a meromictic system with an outlet to the sea allowing denser seawater to
occupy the monimolimnion while the mixolimnion has relatively low salinity and is the site of
greater mixing and microbial activity. The density contrast between the two layers allows for a
unique geochemical environment characterized by steep redox gradients at the interface. This
chemocline is a habitat for magnetotactic bacteria (MB), and the spatial and temporal distribution
of MB in the system along with geochemical (Fe2+, H2S, pH, O2 (aq), etc.) profiles have been
analyzed from 2002 - 2005. It has been previously observed that magnetite-producing cocci
occupy the top of the chemocline and greigite-producing MB occur at the base of the chemocline
and in the sulfidic hypolimnion. This distribution may be attributed to analyte profiles within the
pond; depth profiles show a sudden drop of dissolved oxygen (DO) at the chemocline associated
with an increase in dissolved Fe(II) concentrations that peak where both O2 and H2S are low. In
the sulfidic hypolimnion, Fe(II) concentrations decrease, suggesting buffering of Fe(II) by
sulfide phases. Maximum concentrations of iron (II) and sulfide are ~31 µM and 3 mM,
respectively. Stability diagrams of magnetite and greigite within EH/pH space and measured
voltammetric data verify fields of incomplete oxidation resulting in the production of elemental
sulfur, thiosulfate and polysulfides. Calculations of the Gibbs free energy in the Salt Pond
chemocline for potential microbial redox reaction involving iron and sulfur species indicate
abundant potential energy available for metabolic growth. Oxidation of ferrous iron to
ferrihydrite in the upper region of the chemocline consistently has a yield of over -250 kl/mol O2
(aq), - 12.5 times the proposed 20 kl/mol minimum proposed by Schink (1997) necessary to sustain metabolic growth. This translates into biomass yields of - 0.056 mg dry mass per liter of
upper chemocline water. If these numbers are applied to the dominant bacteria of the chemocline
(MB that are 3% dry weight iron) then there could be up to - 1.68 p.g of iron per liter of upper
chemocline water just in the MB. This iron can be permanently sequestered by MB into the
sediments after death because the organelles containing the iron phases are resistant to
degradation. Geochemical and microbial processes relating to the cycling of iron heavily impact
this system and perhaps others containing a chemocline that divides the water column into oxic
and anoxic zones.
