Methylmercury (MeHg) degradation was investigated along an eutrophicat
ion gradient in the Florida Everglades by quantifying (CH4)-C-14 and (
CO2)-C-14 production after incubation of anaerobic sediments with [C-1
4]MeHg. Degradation rate constants (k) were consistently less than or
equal to 0.1 d(-1) and decreased with sediment depth. Higher k values
were observed when shorter incubation times and lower MeHg amendment l
evels were used, and k increased 2-fold as in-situ MeHg concentrations
were approached. The average flee layer k was 0.046 +/- 0.023 d(-1) (
n = 17) for 1-2 day incubations. In-situ degradation rates were estima
ted to be 0.02-0.5 ng of MeHg (g of dry sediment)(-1) d(-1) increasing
I from eutrophied to pristine areas. Nitrate-respiring bacteria did n
ot demethylate MeHg, and NO3- addition partially inhibited degradation
in some cases. MeHg degradation rates were not affected by PO43- addi
tion. (CO2)-C-14 production in all samples indicated that oxidative de
methylation (OD)was an important degradation mechanism. OD occurred ov
er 5 orders of magnitude of applied MeHg concentration, with lowest li
mits [1-18 ng of MeHg (g of dry sediment)(-1)] in the range of in-situ
MeHg levels. Sulfate reducers and methanogens were the primary agents
of anaerobic OD, although it is suggested that methanogens dominate d
egradation at in-situ MeHg concentrations. Specific pathways of OD by
these two microbial groups are proposed.