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Spatial and temporal variation of biomass in a tropical forest: results from a large census plot in Panama

Journal Article

Chave J; Condit R; Lao S; Caspersen J; Foster R; Hubbell S

2003

Journal of Ecology

91

240-252

We estimated the dry living above-ground biomass (AGB) standing stock and its turnover in a 50-hectare forest plot located in moist tropical forest on Barro Colorado Island Panama. The estimates were obtained using inventory data collected every 5 years from 1985 to 2000 including measurements of all trees 1 cm diameter. 2 Four different allometric regressions relating trunk diameter and height with AGB were compared. Based on the most consistent method we estimated that the Barro Colorado forest holds 281 ± 20 Mg ha1 (1 Mg = 103 kg) of AGB lianas included. A third of the AGB is stored in trees larger than 70 cm in diameter. 3 Stand-level AGB increment (growth plus recruitment) was highest in the period 1985-90 (7.05 ± 0.32 Mg ha1 year1 mean ± 95% confidence limits based on samples of multiple hectares) and smallest in the period 1990-95 (5.25 ± 0.26 Mg ha1 year1) while AGB losses were similar during the three intervals (mean 5.43 ± 0.72 Mg ha1 year1). This resulted in significant differences in AGB change (defined as increment minus loss) among census intervals; including branchfalls the AGB of Barro Colorado Island increased in 1985-90 (+0.82 ± 0.84 Mg ha1 year1) decreased in 1990-95 (0.69 ± 0.82 Mg ha1 year1) and increased again in 1995-2000 (+0.45 ± 0.70 Mg ha1 year1). The 15-year average was +0.20 Mg ha1 year1 but with a confidence interval that spanned zero (0.68 to 0.63 Mg ha1 year1). 4 Branchfalls and partial breakage of stems had a significant influence on the AGB changes. They contributed an average of 0.46 Mg ha1 year1 to the AGB loss. About 5% of AGB increment was due to trees less than 10 cm in diameter. 5 To test whether the AGB of tropical forests is increasing due to climate change we propose that in each forest type at least 10 hectares of forest be inventoried and that measurements of the small classes (< 10 cm diameter) as well as large size classes be included. Biomass loss due to crown damage should also be estimated.

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Support

The Liana Ecology Project is supported by Marquette University and funded in part by the National Science Foundation.