
U.S. Department of the Interior
U.S. Geological Survey
FS-166-96
Mercury Studies in the Florida Everglades
Mercury Cycling in the Florida Everglades
Project
In response to this request from resource managers for more
scientific information on mercury cycling in the Everglades, the
USGS South Florida Ecosystem Program, SFWMD, and USEPA are
co-funding a group of scientists to study mercury bioaccumulation
in the Everglades. Participating scientists are from several
agencies, including: USGS, SFWMD, FDEP, USEPA, Wisconsin
Department of Natural Resources, and University of
Wisconsin-Madison. The overall objective of this project is to
provide resource managers scientific information on the
hydrologic, biologic, and geochemical processes controlling
mercury cycling in the Everglades. It is anticipated, however,
that information from this project will be transferrable to other
ecosystems where mercury problems arise. Specific areas of
research among the group includes: geochemical studies of
mercury, mercury methylation and demethylation studies, DOC-Hg
interactions, mercury accumulation in sediments, diagenetic
processes in peat, sulfur cycling studies, biological uptake of
mercury and lower food chain transfer pathways, and
groundwater/surface-water exchange.
From a resource management perspective, one of the primary
concerns of this project is the long- and short-term effects of
the Everglades Nutrient Removal (ENR) project
(fig. 3), which is a crucial
component of the SFWMD´s restoration plans. The ENR project
calls for the construction of stormwater treatment areas (STAs),
which are reclaimed agricultural lands that will be permanently
flooded with water draining from the EAA and thus reduce
phosphorus loads to the Water Conservation Areas (WCAs) by
sequestering phosphorus through biological uptake. Questions have
arisen concerning whether enhanced mercury methylation might
result within the STAs and present a toxicological hazard for
wildlife residing there, or whether potentially high levels of
CH3Hg+ in outflows from the STAs might present an environmental
hazard to wildlife in the WCAs.
Initially, this project is focusing on field sites in the
northern Everglades
(fig. 4), where phosphorus
loading from the EAA and its impact on mercury cycling is of
concern. Sampling stations include several sites within the ENR,
canals, and marshes. Sites along the L-39 canal were chosen to
examine how mercury levels change with distance from the EAA and
as water leaves the canals through levee spillways and encounters
more quiescent conditions of WCA2. Sites within WCA2 are along a
transect that spans the region of greatest phosphorus impact (as
indicated in the satellite image map,
fig. 4) to the middle of
WCA2 and WCA3 where more natural phosphorus conditions
prevail. The two sites along the L-67 canal were chosen because
this area showed the greatest Hg concentrations in largemouth
bass.
The following are brief descriptions of each of the subprojects
that make up the "Mercury Cycling in the Everglades" project.
Geochemical Process Studies of Mercury
To understand how mercury is transported
and transformed in the environment, a basic understanding of the
spatial occurrence and predominance of the forms of mercury is
necessary. Mercury concentrations in water are so low, however,
that samples collected for this part of the project require the
use of ultra-clean techniques
(fig. 5). Specific study
objectives for this aspect of the project include:
- determination of spatial variability and predominance of the specific forms of mercury in water and suspended particles;
- investigation of the factors controlling the short-term variations in mercury transformation processes;
- examination of factors controlling the spatial and temporal variability of mercury methylation; and
- determination of the important locations and mechanisms of food-chain uptake of mercury.
Methylmercury Degradation Studies
Because methylmercury is the most
bioaccumulative form of mercury and thus the most toxic, it is
important to understand what controls the detoxification process
of demethylation. Scientists currently hold that demethylation
can proceed along two pathways: methyl-cleavage and oxidative
demethylation. The objective of this study is to understand the
environmental factors regulating these two processes.
Dissolved Organic Carbon-Hg Interactions
By effectively binding mercury, DOC provides a mechanism to
mobilize mercury and many other trace metals in the environment
which would otherwise be virtually immobile. This projects seeks
to:
- identify the origin(s) of the DOC in the Everglades system;
- define how the quantity and quality (molecular makeup) of DOC
changes throughout the system;
- determine what controls the reactivity (binding) of mercury
with DOC, and how it varies across the ecosystem; and
- understand how land use and hydrologic changes affect DOC.
Sulfur Cycling Studies
Mercury transport, accumulation, and cycling are controlled by
several microbially mediated processes, many of which are related
to sulfur cycling. Although it is now known that sulfate reducing
bacteria are the principal organisms responsible for mercury
methylation in the Everglades, the relation between sulfur
cycling and mercury methylation is not well understood in
general. The objective of this study is to relate sulfur
reactions and isotopic composition and their relation to changes
in nutrient concentrations, season, rates of sedimentary
deposition, and ultimately to mercury cycling.
Mercury Accumulation and Diagenetic Processes in Peat
Like most wetlands, the Everglades has an accumulation of
surficial peat. Because mercury has a strong affinity for organic
matter, mercury that has accumulated in the peat represents the
vast majority of what is found in the entire ecosystem. Peat
deposits, however, are also known to be areas of significant
physical and chemical change (diagenesis). Many biogeochemical
processes that control the mobility of most nutrients and trace
metals, including mercury, operate in peat. Therefore, it is
important to understanding the processes that result in mercury
accumulation and potential remobilization in peat. The objectives
of this study are to determine the size of the mercury reservoir
within the peat, ascertain how diagenetic processes may be
affecting the stability of this reservoir, and document
historical changes in mercury accumulation rates in the peat.
Biological Uptake of Mercury and Lower Food Chain Transfer Pathways
The assemblage of microalgae that live on shallow submerged
substrates are referred to collectively as periphyton. This
periphyton covers most submerged plants and forms a thick mat on
the sediment surface in many locations in the Everglades. In this
ecosystem, periphyton growth is responsible for the majority of
primary production, and thus is an important food source. The
linkages between the primary producers (periphyton), primary
consumers (invertebrate organisms consuming and living in and
around the periphyton) and secondary consumers (predaceous fish)
are important to document to fully understand how the
bioaccumulation process operates in the Everglades. The
objectives of this study are to:
- determine whether mercury methylation is actively occurring
in the periphyton, and if so, is this mercury being
transferred to the food chain, and
- document the important food chain linkages of mercury
transfer from the primary producers to predaceous fish.
Ground-Water/Surface-Water Exchange
One potentially important source of mercury to the Everglades,
yet currently not quantified, is ground-water discharge. Ground
water also contains other important ingredients for the
methylation process, such as sulfate and DOC. To date, however,
very few studies have examined the nature of
ground-water/surface-water exchange in the Everglades. The
specific objectives of this study are to:
- determine water fluxes and hydraulic properties of sites in
the ENR and WCA2;
- relate those fluxes to hydrogeologic properties, climatic
variability, and water-level management strategies; and
- estimate ground-water fluxes of mercury and nutrients to
surface water.
Next: Anticipated Schedule
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Last updated: 09 November, 2004 @ 10:33 AM(TJE)