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Phosphorus cycling in a small watershed in the Brazilian Cerrado: impacts of frequent burning
Authors:J??lio Carlos Fran?a Resende  Daniel Markewitz  Carlos Augusto Klink  Mercedes Maria da Cunha Bustamante  Eric A Davidson
Institution:1. Departamento de Ecologia, Universidade de Bras??lia, Campus Universit??rio, Asa Norte, Caixa postal 04631, Bras??lia, DF, Brazil, 70919-910
2. Daniel B. Warnell School of Forest Resources, The University of Georgia, Athens, GA, 30605, USA
3. The Woods Hole Research Center, 149 Woods Hole Road, Falmouth, MA, 02540-1644, USA
Abstract:Plant productivity in many tropical savannas is phosphorus limited. The biogeochemical cycling of P in these ecosystems, however, has not been well quantified. In the present study, we characterized P stocks and fluxes in a well-preserved small watershed in the Brazilian Cerrado. As the Cerrado is also a fire-dominated ecosystem, we measured the P stocks and fluxes in a cerrado stricto sensu plot with complete exclusion of fire for 26 years (unburned plot) and then tested some predictions about the impacts of fire impacts on P cycling in an experimental plot that was burned three times since 1992 (burned plot). The unburned area is an ecosystem with large soil stocks of total P (1,151 kg ha?1 up to 50 cm depth), but the largest fraction is in an occluded form. Readily extractable P was found up to 3 m soil depth suggesting that deep soil is more important to the P cycle than has been recognized. The P stock in belowground biomass (0?C800 cm) was 9.9 kg ha?1. Decomposition of fine litter released 0.97 kg P ha?1 year?1. Fluxes of P through bulk atmospheric deposition, throughfall and litter leachate were very low (0.008, 0.006 and 0.028 kg ha?1 year?1, respectively) as was stream export (0.001 kg ha?1 year?1). Immobilization of P by microbes during the rainy season seems to be an important mechanism of P conservation in this ecosystem. Fire significantly increased P flux in litter leachate to 0.11 kg ha?1 year?1, and added 1.2 kg ha?1 of P in ash deposition after fire. We found an increase of P concentration in soil solution at 100 cm depth (from 0.03 ??g l?1 in unburned plot to 0.3 ??g l?1 in the burned plot). In surface soils (0?C10 cm) of the burned plot, fire decreased the concentrations of extractable organic-P fractions, but did not significantly increase inorganic-P fractions. The reduction of extractable soil organic P in the burned plot in topsoil and the increase of P in the soil solution at greater depths indicated a reduction of P availability and may increase P fixation in deep soils. Repeated fire events over the long term may result in significant net loss of available forms of phosphorus from this ecosystem.
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