HR: 16:00h
AN: B14B-01 INVITED [Abstracts]
TI: Estimating Ecosystem Responses to Changes in Mercury Loading: Lessons From the METAALICUS Project
AU: * Krabbenhoft, D P
EM: dpkrabbe@usgs.gov
AF: U.S. Geological Survey, 8505 Research Way, Middleton, WI 53562, United States
AU: Tate, M T
EM: mttate@usgs.gov
AF: U.S. Geological Survey, 8505 Research Way, Middleton, WI 53562, United States
AU: Harris, R
EM: rharris6@cogeco.ca
AF: Tetra Tech, Inc., 180 Forestwood Drive, Oakville, ON L6J4E6, Canada
AU: Heyes, A
EM: heyes@cbl.umces.edu
AF: University of Maryland, Chesapeake Bay Lab, Solomons, MD 20688, United States
AU: Heyes, A
EM: heyes@cbl.umces.edu
AF: University of Alberta, Department of Biology, Edmonton, AL T6G 2E1, Canada
AU: St. Louis, V
EM: Vince.StLouis@ualberta.ca>
AF: University of Alberta, Dept. of Biology, Edmonton, AL T6G 2E1, Canada
AU: Graydon, J
EM: jgraydon@ualberta.ca
AF: University of Alberta, Dept. of Biology, Edmonton, AL T6G 2E1, Canada
AU: Branfireun, B
EM: brian.branfireun@utoronto.ca
AF: University of Toronto at Mississauga, Dept. of Geography, Mississauga, ON L5L1C6,
Canada
AB:
The Mercury Experiment to Assess Atmospheric Loadings in Canada and the US (METAALICUS) project is a
whole-ecosystem, mercury (Hg) loading experiment specifically designed to examine the relation between
atmospheric mercury deposition and fish Hg concentrations. This project was prompted by the observation that
we lacked clear evidence whether a changes atmospheric Hg deposition might lead to a corresponding change
in fish Hg, and at what time scales. To address this information need, a multi-national team of scientists was
formed to devise a whole-ecosystem, Hg-dosing study, whereby mercury would be deliberately added to an entire
watershed. The study is being conducted at the Experimental Lakes Area (ELA), which is located in northwestern
Ontario, Canada. Whole-ecosystem manipulation studies have a distinct advantage over small-scale (lab scale)
studies, in that natural processes and complexities that are present in watersheds are accounted for in the
scientific results. Starting in the spring of 2001, the METAALICUS team been dosing the entire Lake 658
watershed with about 20 ug/m2/y (about 4-5 times the current ambient load). However, the applied Hg is in the
form of enriched stable isotopes that can be analytically distinguished from previously existing ambient Hg, or
currently depositing Hg. Thus, using the applied isotope as a tracer allows for improved insights into process
rates occurring in watersheds that have not been possible heretofore.
One of the greatest areas of uncertainty for making reliable predictions of the environmental response to changes
in atmospheric Hg deposition is quantifying the flux of Hg from terrestrial systems to downstream aquatic
ecosystems. This is especially problematic for settings where terrestrial inputs are similar in scale to
atmospheric deposition or may exceed it. In these cases, it is critical to understand the details of how Hg is
delivered from watersheds and the relative bioavailability of this Hg compared to that from atmospheric
deposition. With this information in hand, improved predictive capability of response times of Lake 658 (and other
similar lakes) can be achieved. Net accumulation of the applied isotope is reflected in the steadily increasing
isotope concentration in terrestrial soils with each year of application (2001-
2004). However, the total soil-mass accumulation of the Hg isotope represents only about a quarter of that which
has been applied. The remaining isotope mass is primarily accounted for by reemission from soils and plants,
interception and storage in the forest canopy, and runoff. The concentration and overall flux rate of the isotope in
runoff has increased about linearly with each year of application, but runoff mass fluxes are small compared to
the isotope application rate (about 1-3 percent). By calibrating a simple numerical soil-box model, we can
estimate the response time of Lake 658 to changes in Hg load, and if the processes operating in this basin are
applicable elsewhere the model will have utility for estimating response times for a wider range of watershed
conditions.
DE: 0428 Carbon cycling (4806)
DE: 0439 Ecosystems, structure and dynamics (4815)
DE: 0461 Metals
DE: 0466 Modeling
SC: Biogeosciences [B]
MN: 2007 Fall Meeting