Lake sediments are significant sinks for carbon both from the landscape and from within the lake (Dean & Gorham 1998); at the same time they are often net sources of carbon to the atmosphere (Cole et al 1994). Recent studies by Aller (1994), Ahlgren et al (1997), Wachniew and Rozanski (1997), Hodell and Schelske (1998), and Hodell et al (1998) have examined and modeled aquatic carbon cycling in terms of biological and chemical processes; however, less attention has been paid to geological aspects, inorganic carbon components (e.g. calcite), and changes in the lake carbon system over time. My study focuses on threshold transitions between IC and OC dominance in order to resolve the relative impacts of production and preservation, biotic changes, chemical and hydrologic shifts, and nutrient loading. The inverse relation of IC and OC holds true for many Minnesota lakes (Dean 1999a), so this detailed study provides a basis for a regional comparative analysis of lower analytical complexity.
Lakes respond rapidly to environmental changes, so their sediments provide
a high-resolution integrative record of productivity, chemistry, climate,
and human impacts in the lake and its watershed. The inherent sensitivity
of small lakes suggests that the abrupt divergence observed in Green and
Spectacle results from a relatively minor shift in some chemical parameter
in one or both of the lakes. An understanding of such threshold behavior
is vital in light of human impacts on lakes and increasing atmospheric
CO2. Algal and microbial photosynthesis in surface waters encourages
carbonate precipitation by drawing down dissolved CO2 and providing
a nucleation site (Hodell et al 1998); oxidation of sinking organic biomass
may deplete bottom water dissolved O2 and increase CO2,
promoting preservation of organic matter and dissolution of carbonates
(Dean 1999a). The respective magnitudes of these fluxes, and the related
interactions between in-lake processes, determine whether the individual
lake is a source or a sink for C, and on a global scale, whether lakes
will buffer the atmosphere or exacerbate the anthropogenic rise in carbon
gases. My calculations give a conservative annual total C burial, at its
maximum in the mid-1950s, of 2.6 x 105 kg C in Green Lake (200
g C m-2 y-1). Though surprisingly large, this figure
is in keeping with the average rate in Minnesota lakes over the past 4000
years calculated by Dean and Gorham (1998) of 81 g C m-2 y-1.
Aller, R.C. 1994. Bioturbation and remineralization of sedimentary organic matter: effects of redox oscillation. Chem. Geol. 114, 331-345.
Bertoni, R., C. Callieri, G. Morabito, M.L. Pinolini, and A. Pugnetti 1997. Quali-quantitative changes in organic carbon production during the oligotrophication of Lake Maggiore, Italy. Verh. Internat. Verein. Limnol. 26, 300-304.
Canfield, D.E. 1994. Factors influencing organic carbon preservation in marine sediments. Chem. Geol. 114, 315-329.
Cole, J.J. and N.F. Caraco 1998. Atmospheric exchange of carbon dioxide in a low-wind oligotrophic lake measured by the addition of SF-6. Limnology and Oceanography 43:4, 647-656. Cole, J.J., N.F. Caraco, G.W. Kling, and T.K. Kratz 1994. Carbon dioxide supersaturation in the surface waters of lakes. Science 265 (9 Sept 94): 1568-1570.
Dean, W.E. 1999a. The carbon cycle and biogeochemical dynamics in lake sediments. Journal of Paleolimnology, in press.
Dean, W.E. 1999b. Characterization of organic matter in lake sediments from Minnesota and Yellowstone National Park. Submitted.
Dean, W.E., and E. Gorham 1998. Magnitude and significance of carbon burial in lakes, reservoirs, and peatlands. Geology 26:6, 535-538.
Driscoll, C.T., S.W. Effler, and S.M. Doerr 1994,. Changes in inorganic carbon chemistry and deposition in Onondaga Lake, New York. Environ. Sci. Technol. 28:7, 1211-1218.
Hartnett, H.E., R.G. Keil, J.I. Hedges, and A.H. Devol 1998. Influence of oxygen exposure time on organic carbon preservation in continental margin sediments. Nature 391, 572-574.
Hodell, D.A. and C.L. Schelske 1998. Production, sedimentation, and isotopic composition of organic matter in Lake Ontario. Limnology and Oceanography 43:2, 200-214.
Hodell, D.A., C.L. Schelske, G.L. Fahnenstiel, and L.L. Robbins 1998. Biologically induced calcite and its isotopic composition in Lake Ontario. Limnology and Oceanography 43:2, 187-199.
Hollander, D.J., and J.A. McKenzie 1991. CO2 control on carbon-isotope fractionation during aqueous photosynthesis: a paleo-CO2 barometer. Geology 19, 929-932.
Kratz, T.K., J. Schindler, D. Hope, J.L. Riera and C.J. Bowser 1997. àTITLE?ß Verh. Internat. Verein. Limnol. 26, 35-338.
Meyers, P.A. and R. Ishiwatari 1993. Lacustrine organic geochemistry - an overview of indicators of organic matter sources and diagenesis in lake sediments. Org. Geochem. 20:7, 867-900.
Molot, L.A. and P.J. Dillon 1996. Storage of terrestrial carbon in boreal lake sediments and evasion to the atmosphere. Global Biogeochemical Cycles 10:3, 483-492.
Raymond, P.A., N.F. Caraco, and J.J. Cole 1997. CO2 concentration and atmospheric flux in the Hudson River. Estuaries 20, 381-390.
Wachniew, P., and K. Róžanski 1997. Carbon budget of a mid-latitude, groundwater-controlled lake: isotopic evidence for the importance of dissolved inorganic carbon recycling. Geochim. Cosmochim. Acta 61:12, 2453-2465.
Winter, T.C., ed., 1997. Hydrological and Biogeochemical Research in
the Shingobee River Headwaters Area, North-Central Minnesota. U.S. Geological
Survey Water-Resources Investigations Special Report 96-4215.
A version of this project description appeared in a successful application for GSA Student Research funds in 1999.