| |
We
surveyed bays on the Savannah River Site (SRS), an 800 km2 federal
reservation located in south-central South Carolina. Public access
to the SRS has been restricted since the 1950s, and the land consists
of abandoned farms, and pine and deciduous forests. |
|
a |
| |
Over
300 Carolina bays exist on the SRS; previous studies have documented
flora and fauna and followed long-term changes in these systems,
but no previous work has been done on mercury or other heavy metals
in these systems. |
|
a |
| |
There
are no point sources or history of Hg pollution in the watersheds
of any of these bays, suggesting the importance of atmospheric inputs.
|
|
a |
| |
Three
species were common to most bays: lake chubsucker (Erimyzon sucetta),
mud sunfish (Acantharchus pomotis) , and redfin pickerel (Esox americanus).
|
|
|
| |
Fish
lengths were chosen based on stork diet data presented in Gariboldi
et al., (1998); these sizes represent typical fish from these wetlands
that might be consumed by predators foraging in the bays. |
|
a |
| |
Fish
(total n about 300) were collected using minnow traps and hoop traps
from March - June 1997. |
|
a |
| |
Water
samples were also collected for analysis of major anions and cations,
and hydro period and maximum depth were determined on repeat visits
over a multi-year period. |
|
a |
| |
Fish
were freeze-dried to determine moisture content, then digested digested
in sealed teflon vessels in a microwave oven, diluted with high-purity
deionized water and assayed for Hg within 48 hours. |
|
a |
| |
Mercury
was determined by cold-vapor atomic fluorescence detection. |
|
|
| |
Over
25 % of all samples were spikes, blanks, replicates, or standard
materials with certified mercury concentrations (National Research
Council of Canada). |
| |
a |
| |
Spike
recovery averaged 95 % (n=40); differences between replicates 8
% (n = 78). |