Abstract
The sediment record from a 5.3-m core from Sargent Mountain Pond, Maine USA indicates strong co-evolutionary relationships among climate, vegetation, soil development, runoff chemistry, lake processes, diatom community, and water and sediment chemistry. Early post-glacial time (16,600–12,500 Cal Yr BP) was dominated by deposition of mineral-rich sediment, low in organic matter and secondary hydroxides of Al and Fe; pollen indicate tundra conditions; diatom taxa indicate pH between 7.5 and 8, and total P concentrations of about 25 μg L−1, favoring higher productivity. Chemical weathering was rapid, with high alkalinity, pH, Ca, and P in runoff. As climate ameliorated, about 12,500 Cal Yr BP, forest vegetation became established; soils would have developed vertical zonation, including organic matter accumulation, and incipient podzolic horizons, with accumulating secondary hydroxides of Al and Fe that sequestered P in the soils. Labile minerals (primarily apatite, Ca5(PO4)3(OH,F,Cl)) became depleted in the soil, further reducing the supply of P to the lake. Dissolved organic carbon (DOC) from soil organic matter mobilized Al and Fe to the lake where Al(OH)3 (primarily) and Fe(OH)3 (minor) were precipitated. The sedimenting hydroxides adsorbed P from the water column, further reducing bioavailable P. These long-term trends of moderating climate, and changing terrestrial biology, soils, and aquatic chemistry and phytoplankton were interrupted by the 1,000-year long Younger Dryas cooling, which led to a temporary reversal of these processes, a period that ended with the major onset of Holocene warming. The sequestration of P by soils would have strengthened because of long-term soil acidification and pedogenesis. The lake was transformed from a more productive, high P, high pH, low DOC system into an oligotrophic, relatively low P, acidic, humic lake over a period of 16,600 years, a natural trend that continues. In contrast to many human-affected lakes that become increasingly eutrophic, many lakes become more oligotrophic during their history. The precursors for that are: (1) absence of human land-use in watersheds, (2) bedrock lithology and soil with a paucity of soluble Ca-rich minerals, and (3) vegetation that promotes the accumulation of soil organic matter, podzolization, and increased export of metal-DOC complexes, particularly Al.
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Acknowledgments
Our research was supported by National Science Foundation grants DEB-0415348 and DEB-0414144 to Norton and Fernandez, respectively, and by a gift from Nestlé Waters of North America to Norton. We greatly appreciate the support of staff at Acadia National Park. John Cangelosi, Ben Gross, David Huntress, and Cindy Loften assisted in coring. Processing of the core at the University of Maine was by Andrea Nurse, Robert Harrington, and Samuel Roy. Bekka Brodie provided excellent analytical capabilities. We thank Brian Ginn for applying the pH and total phosphorus models to our fossil diatom data. Richard Bindler kindly provided us with output from the CLAM chronology model (Blaauw 2010). We appreciate the thoughtful, thorough, and constructive reviews of John A. Boyle and one anonymous reviewer, who patiently offered excellent advice on two iterations. Their suggestions substantially improved the clarity of our presentation, and allowed us to correct errors and sharpen the science.
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Norton, S.A., Perry, R.H., Saros, J.E. et al. The controls on phosphorus availability in a Boreal lake ecosystem since deglaciation. J Paleolimnol 46, 107–122 (2011). https://doi.org/10.1007/s10933-011-9526-9
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DOI: https://doi.org/10.1007/s10933-011-9526-9