OOS 36-4 - Size, species, and fire behaviour predict tree and liana mortality from experimental burns in the Brazilian Amazon

Thursday, August 11, 2011: 9:00 AM
12A, Austin Convention Center
Jennifer K. Balch1, Daniel C. Nepstad2, Lisa M. Curran3, Paulo M. Brando4, Osvaldo Portela2, Paulo G.P. dos Santos5, Jonathan D. Reuning-Scherer6 and Oswaldo Carvalho7, (1)Earth Lab, University of Colorado-Boulder, Boulder, CO, (2)Instituto de Pesquisa Ambiental da Amazônia (Amazon Institute of Environmental Research), Belém, Brazil, (3)Stanford University, Stanford, CA, (4)Instituto de Pesquisa Ambiental da Amazônia (IPAM), Brasília, Brazil, (5)Universidade Federal do Pará, Belém, Brazil, (6)Yale University, New Haven, CT, (7)Instituto de Pesquisa Ambiental da Amazônia (Amazon Institute of Environmental Research), Brasilia, Brazil

Anthropogenic understory fires have affected large areas of tropical forest in recent decades, particularly during severe droughts. Yet, the mechanisms that control fire-induced mortality of tropical trees and lianas remain ambiguous due to the challenges associated with documenting mortality given variation in fire behavior and forest heterogeneity. In a seasonally dry Amazon forest, we conducted a burn experiment to quantify how increasing understory fires alter patterns of stem mortality. From 2004 to 2007, tree and liana mortality was measured in adjacent 50-ha plots that were intact (B0–control), burned once (B1), and burned annually for 3 years (B3).


After 3 years, cumulative tree and liana mortality (>=1cm dbh) in the B1 (5.8% yr−1) and B3 (7.0% yr−1) plots significantly exceeded mortality in the control (3.2% yr−1). However, these fire-induced mortality rates are substantially lower than those reported from more humid Amazonian forests. Small stems were highly vulnerable to fire-induced death, contrasting with drought-induced mortality (measured in other studies) that increases with tree size. For example, one low-intensity burn killed >50% of stems <10cm within a year. Independent of stem size, species-specific mortality rates varied substantially from 0% to 17% yr−1 in the control, 0% to 26% yr−1 in B1, and 1% to 23% yr−1 in B3, with several species displaying high variation in their vulnerability to fire-induced mortality. Protium guianense (Burseraceae) exhibited the highest fire-induced mortality rates in B1 and B3, which were 10- and 9-fold greater than the baseline rate. In contrast, Aspidosperma excelsum (Apocynaceae), appeared relatively unaffected by fire (0.3% to 1.0% mortality yr−1 across plots), which may be explained by fenestration that protects the inner concave trunk portions from fire. For stems >=10 cm, both char height (approximating fire intensity) and number of successive burns were significant predictors of fire-induced mortality, whereas only the number of consecutive annual burns was a strong predictor for stems <10 cm. Three years after the initial burn, 62 ±26 Mg ha−1 (s.e.) of live biomass, predominantly stems <30 cm, was transferred to the dead biomass pool, compared with 8 ±3 Mg ha−1 in the control. This biomass loss from fire represents around 30% of this forest’s aboveground live biomass (192 (±3) Mg ha−1; >1cm DBH). Although forest transition to savanna has been predicted based on future climate scenarios, our results indicate that wildfires from agricultural expansion pose a more immediate threat to the current carbon stocks in Amazonian forests.

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