2 research outputs found
ENSO Drives interannual variation of forest woody growth across the tropics
Meteorological extreme events such as El Niño events are expected to affect tropical forest net primary production (NPP) and woody growth, but there has been no large-scale empirical validation of this expectation. We collected a large high–temporal resolution dataset (for 1–13 years depending upon location) of more than 172 000 stem growth measurements using dendrometer bands from across 14 regions spanning Amazonia, Africa and Borneo in order to test how much month-to-month variation in stand-level woody growth of adult tree stems (NPPstem) can be explained by seasonal variation and interannual meteorological anomalies. A key finding is that woody growth responds differently to meteorological variation between tropical forests with a dry season (where monthly rainfall is less than 100 mm), and aseasonal wet forests lacking a consistent dry season. In seasonal tropical forests, a high degree of variation in woody growth can be predicted from seasonal variation in temperature, vapour pressure deficit, in addition to anomalies of soil water deficit and shortwave radiation. The variation of aseasonal wet forest woody growth is best predicted by the anomalies of vapour pressure deficit, water deficit and shortwave radiation. In total, we predict the total live woody production of the global tropical forest biome to be 2.16 Pg C yr−1, with an interannual range 1.96–2.26 Pg C yr−1 between 1996–2016, and with the sharpest declines during the strong El Niño events of 1997/8 and 2015/6. There is high geographical variation in hotspots of El Niño–associated impacts, with weak impacts in Africa, and strongly negative impacts in parts of Southeast Asia and extensive regions across central and eastern Amazonia. Overall, there is high correlation (r = −0.75) between the annual anomaly of tropical forest woody growth and the annual mean of the El Niño 3.4 index, driven mainly by strong correlations with anomalies of soil water deficit, vapour pressure deficit and shortwave radiation
What controls variation in carbon use efficiency among Amazonian tropical forests?
Why do some forests produce biomass more efficiently than others? Variations in Carbon Use Efficiency (CUE: total Net Primary Production (NPP)/ Gross Primary Production (GPP)) may be due to changes in wood residence time (Biomass/NPPwood), temperature, or soil nutrient status. We tested these hypotheses in 14, one ha plots across Amazonian and Andean forests where we measured most key components of net primary production (NPP: wood, fine roots, and leaves) and autotrophic respiration (Ra; wood, rhizosphere, and leaf respiration). We found that lower fertility sites were less efficient at producing biomass and had higher rhizosphere respiration, indicating increased carbon allocation to belowground components. We then compared wood respiration to wood growth and rhizosphere respiration to fine root growth and found that forests with residence times 40 yrs. A comparison of rhizosphere respiration to fine root growth showed that rhizosphere growth respiration was significantly greater at low fertility sites. Overall, we found that Amazonian forests produce biomass less efficiently in stands with residence times >40 yrs and in stands with lower fertility, but changes to long-term mean annual temperatures do not impact CUE.This work is a product of the Global Ecosystems
Monitoring (GEM) network (gem.tropicalforests.ox.ac.uk) the
Andes Biodiversity and Ecosystems Research Group ABERG
(andesresearch.org) and the Amazon Forest Inventory Network
RAINFOR (www.rainfor.org) research consortia, and was funded
by grants from the UK Natural Environment Research Council
(Grants NE/D01025X/1, NE/D014174/1), grants to YM and
OP from the Gordon and Betty Moore Foundation, and a grant
from the EU FP7 GEOCARBON (283080) project. We thank
the Servicio Nacional de Areas Naturales Protegidas por el
Estado (SERNANP) and personnel of Manu National Park who
provided logistical assistance and permission to work in the pro-
tected areas in Peru, the Explorers’ Inn at Tambopata, ACCA for
use of the Wayqecha Research Station, and IIAP for use of the
Allpahuayo Research Station, the Museo Goeldi for access to the
Caxiuan~a Research Station, and IPAM for the access to the Tan-
guro plots. We also gratefully acknowledge LBA support CNPQ
grant 411 457914/2013-0/MCTI/CNPq/FNDCT/LBA/ESE-
CAFLOR to ACLD, and NERC and ARC support to PM (NE/
J011002/1, DP170104091). YM is supported by an ERC
Advanced Investigator Award GEM-TRAIT (321131) and by the
Jackson Foundation. CED is supported by the John Fell Fund
and Google