Title
Peatland forests are the least diverse tree communities documented in Amazonia, but contribute to high regional beta-diversity
Date Issued
01 August 2018
Access level
open access
Resource Type
journal article
Author(s)
Draper F.C.
Roucoux K.H.
Lawson I.T.
Nigel N.C.
Paul P.V.
Phillips O.L.
Torres Montenegro L.A.
Valderrama Sandoval E.
Mesones I.
Arévalo F.R.R.
Baker T.R.
Publisher(s)
Blackwell Publishing Ltd
Abstract
Western Amazonia is known to harbour some of Earth's most diverse forests, but previous floristic analyses have excluded peatland forests which are extensive in northern Peru and are among the most environmentally extreme ecosystems in the lowland tropics. Understanding patterns of tree species diversity in these ecosystems is important both for quantifying beta-diversity in this region, and for understanding determinants of diversity more generally in tropical forests. Here we explore patterns of tree diversity and composition in two peatland forest types – palm swamps and peatland pole forests – using 26 forest plots distributed over a large area of northern Peru. We place our results in a regional context by making comparisons with three other major forest types: terra firme forests (29 plots), white-sand forests (23 plots) and seasonally-flooded forests (11 plots). Peatland forests had extremely low (within-plot) alpha-diversity compared with the other forest types that were sampled. In particular, peatland pole forests had the lowest levels of tree diversity yet recorded in Amazonia (20 species per 500 stems, Fisher's alpha 4.57). However, peatland pole forests and palm swamps were compositionally different from each other as well as from other forest types in the region. Few species appeared to be peatland endemics. Instead, peatland forests were largely characterised by a distinctive combination of generalist species and species previously thought to be specialists of other habitats, especially white-sand forests. We suggest that the transient nature and extreme environmental conditions of Amazonian peatland ecosystems have shaped their current patterns of tree composition and diversity. Despite their low alpha-diversity, the unique combination of species found in tree communities in Amazonian peatlands augment regional beta-diversity. This contribution, alongside their extremely high carbon storage capacity and lack of protection at national level, strengthens their status as a conservation priority.
Start page
1256
End page
1269
Volume
41
Issue
8
Language
English
OCDE Knowledge area
Ecología
Forestal
Scopus EID
2-s2.0-85040693733
Source
Ecography
ISSN of the container
09067590
Sponsor(s)
Acknowledgements – We would like to thank the following people for their assistance during the peatland fieldwork in Peru: Julio Irarica, Hugo Vasquez, Massiel Corrales, Darcy García, Cecilia Ballón, Luisa Huaratapairo, Carlos Mogollon, Sarah Pearl, Esme Shattock, and Oliver Clark. We also thank the following people who were involved in collecting the ‘terra firme’ dataset: Rodolfo Vásquez-Martínez, Hugo Mogollón, Nállarett Dávila, Marcos Ríos, Juan Guevara, Abel Monteagudo, Manuel Ahuite, Milton Aulestia, Dairon Cárdenas, Carlos E. Cerón, Pierre-André Loizeau, David A. Neill, Percy Núñez V., Walter A. Palacios, and Rodolphe Spichiger. We thank Dennis Del Castillo, Ricardo Farroñay and Jhon del Águila from IIAP for their help with logistics during the peatland fieldwork. We also thank the communities of Veinte de Enero, Ollanta, Miraflores, Nueva York, San Roque, Santa Rita, Buena Vista, Parinari, Jenaro Herrera, Saramuro and San Jorge. Funding – FCD was supported by a NERC PhD Studentship (NE/ J50001X/1). Additional funding for the peatland fieldwork and floristic assessment was provided by a NERC Small Grant to KHR, TRB and IL (NE/H011773/1), The Royal Geographical Society, The Quaternary Research Association, The Anglo-Peruvian Society, the Earth and Space Foundation, and the Inst. de Investigaciones de la Amazonía Peruana. Plot installation, fieldwork and botanical identification in RAINFOR plots has been supported by several grants including a Gordon and Betty Moore Foundation grant to RAINFOR, the EU’s Seventh Framework Programme (283080, ‘GEOCARBON’) and NERC grants to OLP (grants NER/ A/S/2000/0053, NE/B503384/1, NE/F005806/1, and a NERC Postdoctoral Fellowship), and a National Geographic Society for supporting forest dynamics research in Amazonian Peru (grant #5472-95). OLP is supported by an ERC Advanced Grant and is a Royal Society-Wolfson Research Merit Award holder. TRB acknowledges support from a Leverhulme Research Fellowship (RF-2015-653). Permits – We thank SERNANP and SERFOR for providing research permits to work inside and outside protected areas.
Funding ? FCD was supported by a NERC PhD Studentship (NE/J50001X/1). Additional funding for the peatland fieldwork and floristic assessment was provided by a NERC Small Grant to KHR, TRB and IL (NE/H011773/1), The Royal Geographical Society, The Quaternary Research Association, The Anglo-Peruvian Society, the Earth and Space Foundation, and the Inst. de Investigaciones de la Amazon?a Peruana. Plot installation, fieldwork and botanical identification in RAINFOR plots has been supported by several grants including a Gordon and Betty Moore Foundation grant to RAINFOR, the EU's Seventh Framework Programme (283080, ?GEOCARBON?) and NERC grants to OLP (grants NER/A/S/2000/0053, NE/B503384/1, NE/F005806/1, and a NERC Postdoctoral Fellowship), and a National Geographic Society for supporting forest dynamics research in Amazonian Peru (grant #5472-95). OLP is supported by an ERC Advanced Grant and is a Royal Society-Wolfson Research Merit Award holder. TRB acknowledges support from a Leverhulme Research Fellowship (RF-2015-653). Permits ? We thank SERNANP and SERFOR for providing research permits to work inside and outside protected areas.
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