Philippe Choler

Dr. Philippe Choler

orcid

Research Focus & Metrics

Academic Career Length

31Years (1996-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 June 2002 in Nature
Verified
Journal Article
Closed access
RCRagan M. Callaway
Ragan M. Callaway
RBR. W. Brooker
R. W. Brooker
PCPhilippe Choler
Philippe Choler
ZKZaal Kikvidze
Zaal Kikvidze
CJ LortieCJ Lortie
CJ Lortie
BCBradley J. Cook
Bradley J. Cook

24 December 2010 in Global Change Biology
Verified
Journal Article
Closed access
PDF file
RERobin Engler
Robin Engler
CRChristophe F. Randin
Christophe F. Randin
WTWilfried Thuiller
Wilfried Thuiller
SDStefan Dullinger
Stefan Dullinger
NZNiklaus Zimmermann
Niklaus Zimmermann
AGAntoine Guisan
Antoine Guisan

1 January 2014 in Ecology
Verified
Journal Article
Open access
PDF file
SDStéphane Dray
Stéphane Dray
PCPhilippe Choler
Philippe Choler
SDSylvain Dolédec
Sylvain Dolédec
PPPedro R. Peres-Neto
Pedro R. Peres-Neto
WTWilfried Thuiller
Wilfried Thuiller
CBCajo J. F. ter Braak
Cajo J. F. ter Braak
Assessing trait responses to environmental gradients requires the simultaneous analysis of the information contained in three tables: L (species distribution across samples), R (environmental characteristics of samples), and Q (species traits). Among the available methods, the so‐called fourth‐corner and RLQ methods are two appealing alternatives that provide a direct way to test and estimate trait–environment relationships. Both methods are based on the analysis of the fourth‐corner matrix, which crosses traits and environmental variables weighted by species abundances. However, they differ greatly in their outputs: RLQ is a multivariate technique that provides ordination scores to summarize the joint structure among the three tables, whereas the fourth‐corner method mainly tests for individual trait–environment relationships (i.e., one trait and one environmental variable at a time). Here, we illustrate how the complementarity between these two methods can be exploited to promote new ecological knowledge and to improve the study of trait–environment relationships. After a short description of each method, we apply them to real ecological data to present their different outputs and provide hints about the gain resulting from their combined use.

13 September 2004 in Oikos
Verified
Journal Article
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CJ LortieCJ Lortie
CJ Lortie
RBRob W. Brooker
Rob W. Brooker
PCPhilippe Choler
Philippe Choler
ZKZaal Kikvidze
Zaal Kikvidze
RMRichard Michalet
Richard Michalet
RCRagan M. Callaway
Ragan M. Callaway

11 February 2022 in Global Change Biology
Verified
Journal Article
Open access
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JLJonas Lembrechts
Jonas Lembrechts
JHJohan van Den Hoogen
Johan van Den Hoogen
JAJuha Aalto
Juha Aalto
MAMichael B. Ashcroft
Michael B. Ashcroft
PFPieter De Frenne
Pieter De Frenne
JLJonathan Lenoir
Jonathan Lenoir
Research in global change ecology relies heavily on global climatic grids derived from estimates of air temperature in open areas at around 2 m above the ground. These climatic grids do not reflect conditions below vegetation canopies and near the ground surface, where critical ecosystem functions occur and most terrestrial species reside. Here, we provide global maps of soil temperature and bioclimatic variables at a 1‐km2resolution for 0–5 and 5–15 cm soil depth. These maps were created by calculating the difference (i.e. offset) between in situ soil temperature measurements, based on time series from over 1200 1‐km2pixels (summarized from 8519 unique temperature sensors) across all the world's major terrestrial biomes, and coarse‐grained air temperature estimates from ERA5‐Land (an atmospheric reanalysis by the European Centre for Medium‐Range Weather Forecasts). We show that mean annual soil temperature differs markedly from the corresponding gridded air temperature, by up to 10°C (mean = 3.0 ± 2.1°C), with substantial variation across biomes and seasons. Over the year, soils in cold and/or dry biomes are substantially warmer (+3.6 ± 2.3°C) than gridded air temperature, whereas soils in warm and humid environments are on average slightly cooler (−0.7 ± 2.3°C). The observed substantial and biome‐specific offsets emphasize that the projected impacts of climate and climate change on near‐surface biodiversity and ecosystem functioning are inaccurately assessed when air rather than soil temperature is used, especially in cold environments. The global soil‐related bioclimatic variables provided here are an important step forward for any application in ecology and related disciplines. Nevertheless, we highlight the need to fill remaining geographic gaps by collecting more in situ measurements of microclimate conditions to further enhance the spatiotemporal resolution of global soil temperature products for ecological applications.

3 February 2014 in Nature Communications
Verified
Journal Article
Closed access
PDF file
Charline Giguet-CovexCharline Giguet-Covex
Charline Giguet-Covex
JPJohan Pansu
Johan Pansu
Fabien ArnaudFabien Arnaud
Fabien Arnaud
PRPierre-Jérôme Rey
Pierre-Jérôme Rey
CGChristophe Griggo
Christophe Griggo
PTPierre Taberlet
Pierre Taberlet