Testing the Amazon savannization hypothesis: fire effects on invasion of a neotropical forest by native cerrado and exotic pasture grasses
Divino V. Silvrio
Paulo M. Brando
Jennifer K. Balch
Francis E. Putz
Daniel C. Nepstad
Claudinei Oliveira-Santos
Mercedes M. C. Bustamante
0
Woods Hole Research Center
,
149 Woods Hole Road, Falmouth, MA 02450
,
USA
1
Instituto de Pesquisa Ambiental da Amazonia
,
Forest Ecology Bele m, Bele m, Para
,
Brazil
2
Departamento de Ecologia Bras lia, Universidade de Bras lia
,
Brasilia, Distrito Federal
,
Brazil
3
Department of Biology, University of Florida
,
Gainesville, FL 32611-8525
,
USA
4
Department of Geography, The Pennsylvania State University
,
Walker Building, University Park, PA 16802
,
USA
5
Department of Global Ecology, Carnegie Institution
,
Stanford, CA 94305-4101
,
USA
Testing the Amazon savannization hypothesis: fire effects on invasion of a neotropical forest by native cerrado and exotic pasture grasses Articles on similar topics can be found in the following collections ecology (543 articles) environmental science (287 articles) plant science (94 articles) Receive free email alerts when new articles cite this article - sign up in the box at the top right-hand corner of the article or click here
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Cite this article: Silverio DV, Brando PM,
Balch JK, Putz FE, Nepstad DC, Oliveira-Santos
C, Bustamante MMC. 2013 Testing the Amazon
savannization hypothesis: fire effects on
invasion of a neotropical forest by native cerrado
and exotic pasture grasses. Phil Trans R Soc B
368: 20120427.
http://dx.doi.org/10.1098/rstb.2012.0427
One contribution of 18 to a Theme Issue
Ecology, economy, and management of an
agroindustrial frontier landscape in the
southeast Amazon.
Subject Areas:
ecology, environmental science, plant science
Author for correspondence:
Divino V. Silverio
e-mail:
Electronic supplementary material is available
at http://dx.doi.org/10.1098/rstb.2012.0427 or
via http://rstb.royalsocietypublishing.org.
Testing the Amazon savannization
hypothesis: fire effects on invasion of a
neotropical forest by native cerrado and
exotic pasture grasses
Divino V. Silverio1,2, Paulo M. Brando2,3,4, Jennifer K. Balch5, Francis E. Putz6,
Daniel C. Nepstad2, Claudinei Oliveira-Santos2 and Mercedes
M. C. Bustamante1
Changes in climate and land use that interact synergistically to increase fire
frequencies and intensities in tropical regions are predicted to drive forests to
new grass-dominated stable states. To reveal the mechanisms for such a
transition, we established 50 ha plots in a transitional forest in the southwestern
Brazilian Amazon to different fire treatments (unburned, burned annually
(B1yr) or at 3-year intervals (B3yr)). Over an 8-year period since the
commencement of these treatments, we documented: (i) the annual rate of
pasture and native grass invasion in response to increasing fire frequency;
(ii) the establishment of Brachiaria decumbens (an African C4 grass) as a
function of decreasing canopy cover and (iii) the effects of grass fine fuel on fire
intensity. Grasses invaded approximately 200 m from the edge into the
interiors of burned plots (B1yr: 4.31 ha; B3yr: 4.96 ha) but invaded less
than 10 m into the unburned plot (0.33 ha). The probability of B. decumbens
establishment increased with seed availability and decreased with leaf area
index. Fine fuel loads along the forest edge were more than three times
higher in grass-dominated areas, which resulted in especially intense fires.
Our results indicate that synergies between fires and invasive C4 grasses
jeopardize the future of tropical forests.
1. Introduction
In many parts of the world, tropical forest savannah boundaries shift in response
to changing climate and disturbance regimes [1,2]. In the southern Amazon Basin,
forest is predicted to retreat owing to climate change [3,4] and land-use practices
[5,6], which may also facilitate grass invasion and increase both the frequencies
and intensities of wildfires. Although some dynamic global vegetation models
predict a late-century Amazonian forest dieback [7,8], an integrated view of how this
process will occur is still lacking. One potent driver could be the increased forest
edge invasion of exotic grasses that accompanies pasture expansion [5]. In
addition, fires reportedly interact with grass invasion through a positive feedback
cycle, which causes a decline in tree cover, facilitates grass invasion and increases
the likelihood of future fires [9 11].
Grass fire cycles are important on many forest frontiers owing to the
combination of increased ignitions, drier forest edges and proliferation of flammable
species. For example, several studies document that establishment of invasive
grasses, which benefits from reduced tree cover [6,12], increases fine fuel
loads, fire intensities [13,14] and grass expansion [6,12 14]. Moreover,
frequently burned forests lose carbon storage capacity and may remain in a
& 2013 The Author(s) Published by the Royal Society. All rights reserved.
BARE SEED control
LAI m2 m2
degraded, low-carbon forest state in which they are
susceptible to recurrent fires [15].
There is a wealth of knowledge about forest savannah
boundary dynamics around the world and about how
introduced grasses alter vegetation and help create new fire cycles
[1,12,13,16]. However, the mechanisms by which grasses
expand at the expense of forests are less well understood
(but see [11]). In the southeastern Amazon, agricultural
expansion [17], selective logging [18] and other land uses may
accelerate the rate of reduction of forest cover and enhance
the fire grass cycle by: (i) reducing tree cover and exposing
vulnerable forest edges [10,19 21]; (ii) introducing propagules
of exotic pasture grasses [11,22]; and (iii) increasing ignitions
associated with land management practices [18,23].
Although the importance of fire grass feedbacks for
tropical forests and savannahs is well established [6,9 14], little is
known about the mechanisms by which grasses invade forests.
In particular, the species composition, extent and fire-related
traits that facilitate this process along the substantial amount
of degraded forest edges created annually by deforestation
need to be documented. In this study, we experimentally
evaluated how two fire frequencies (an annual and triennial burn)
and the resulting differences in canopy cover interact with
grass invasion to change fire behaviour. Specifically, we tested
the predictions that: (i) native cerrado (Brazilian savannah)
and exotic pasture grass invasion of forests from the edge
increases with increases in fire frequency and associated
increases in light availability; (ii) the establishment of the
exotic grass Brachiaria decumbens from seeds experimentally
sown in the forest interior (250 m from forest edges) increases
with canopy openness; and (iii) the presence of exotic grasses
increases forest fire intensity.
2. Material and methods
(a) Study area
In 2004, we established a (...truncated)