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Forest Ecology and Management 255 (2008) 2577-2588
Forest Ecology
and
Management
www.elsevier.com/locate/foreco
Linking tree biodiversity to belowground process in a young tropical
plantation: Impacts on soil C0
2
flux
Meaghan Murphy
a
*, Teri Balser
b
, Nina Buchmann
c
, Volker Hahn
c
, Catherine Potvin
d
'
e
a
Department of Geography, McGill University, 805 Sherbrooke Street West, Montreal, Quebec, Canada H3A 2K6
Department of Soil Science, University of Wisconsin, 1525 Observatory Drive, Madison, WI53706, USA
c
Institute of Plant Sciences, ETH Zurich, LFW, C56, 8092 Zurich, Switzerland
Smithsonian Tropical Research Institute, Panama, Panama
"Department of Biology, McGill University, 1205 Dr. Penfield, Montreal H3A-1B1, Quebec, Canada
Received 4 June 2007; received in revised form 2 January 2008; accepted 9 January 2008
Abstract
This study examined the effect of tree species identity and diversity on soil respiration in a 3-year-old tropical tree biodiversity plantation in
Central Panama. We hypothesized that tree pairs in mixed-species plots would have higher soil respiration rates than those in monoculture plots as a
result of increased primary productivity and complementarity leading to greater root and microbial biomass and soil respiration. In addition to soil
respiration, we measured potential controls including root, tree, and microbial biomass, soil moisture, surface temperature, bulk density. Over the
courseof the wet season, soil respiration decreased from the June highs (7.2 ± 3.5 (Jtmol C02/(m s~ ) toalowof 2.3 ± 1.9 |xmol C02/(m s~ )in
the last 2 weeks of October. The lowest rates of soil respiration were at the peak of the dry season (1.0 ± 0.7 jjtmol CO;/(m^ s
-1
)). Contrary to our
hypothesis, soil respiration was 19-31% higher in monoculture than in pairs and plots with higher diversity in the dry and rainy seasons. Although
tree biomass was significantly higher in pairs and plots with higher diversity, there were no significant differences in either root or microbial
biomass between monoculture and two-species pairs. Path analyses allow the comparison of different pathways relating soil respiration to either
biotic or abiotic controls factors. The path linking crown volume to soil temperature then respiration has the highest correlation, with a value of
0.560, suggesting that canopy controls on soil climate may drive soil respiration.
© 2008 Elsevier B.V. All rights reserved.
Keywords: Biodiversity; Carbon cycling; Ecosystem function; Soil respiration; Tropics
1. Introduction
Covering 40% of the world's land area, tropical systems
house more than half of the terrestrial biomass and one third of
soil carbon (C) while harboring as much as 65% of all species
on earth (Buchmann et al., 2004; Lambertini, 2000). The
tropics thus play a central role in the global C cycle (Knorr,
2000; Rayner et al., 2005). In particular, where there are high
rates of land-use change, both biodiversity and terrestrial C
reserves are decreasing. Until recently rising extinction rates
and global climatic change have been studied separately but
there is growing recognition of the potential feedbacks between
these environmental perturbations (Chapin et al., 2000; Potvin
et al., 2005; Sala et al., 2000; Thomas et al., 2004; Walther,
* Corresponding author. Tel.: +1 514 398 4111; fax: +1 514 398 7437.
E-mail address: mtmurphy_2000@yahoo.com (M. Murphy).
0378-1127/$ - see front matter © 2008 Elsevier B.V. All rights reserved.
doi:10.1016/j.foreco.2008.01.034
2003). Despite the importance of tropical systems most
research integrating biodiversity and C cycling research has
focused on temperate ecosystems neglecting the tropics (Raich
and Schlesinger, 1992; Schimel et al., 2001).
The most current figures indicate that tropical land-use
change has resulted in emission of CC_ on the order of +1 to
2 Gt C year
-
in the last decade (Houghton, 2005) and
approximately 136 ± 55 Gt C year
-1
in terrestrial systems
globally since the onset of the industrial revolution (Houghton,
1999). This amounts to roughly 20% of global greenhouse gas
emissions (GHG). As a result of land-use changes including
deforestation, biomass burning, plowing, and wetland drainage,
terrestrial soils have historically released an estimated 40 Gt
soil organic carbon, primarily via soil respiration (Houghton,
1999). Almost 10% of atmospheric CO2 passes through
soils each year (Raich and Potter, 1995). In terrestrial systems,
soil respiration, the combined CC_ efflux of microbial and
roots respiration from soils, release 50-75 Gt C year
-
to the