Marco Caccianiga

Dr. Marco Caccianiga


Research Focus & Metrics

Academic Career Length

26Years (2001-Present)

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

Representative Publications

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31 December 2019 in Global Change Biology
Verified
Journal Article
Open access
JKJens Kattge
Jens Kattge
GBGerhard Bönisch
Gerhard Bönisch
SDSandra Díaz
Sandra Díaz
SLSandra Lavorel
Sandra Lavorel
IPIain Colin Prentice
Iain Colin Prentice
CWChristian Wirth
Christian Wirth
Plant traits—the morphological, anatomical, physiological, biochemical and phenological characteristics of plants—determine how plants respond to environmental factors, affect other trophic levels, and influence ecosystem properties and their benefits and detriments to people. Plant trait data thus represent the basis for a vast area of research spanning from evolutionary biology, community and functional ecology, to biodiversity conservation, ecosystem and landscape management, restoration, biogeography and earth system modelling. Since its foundation in 2007, the TRY database of plant traits has grown continuously. It now provides unprecedented data coverage under an open access data policy and is the main plant trait database used by the research community worldwide. Increasingly, the TRY database also supports new frontiers of trait‐based plant research, including the identification of data gaps and the subsequent mobilization or measurement of new data. To support this development, in this article we evaluate the extent of the trait data compiled in TRY and analyse emerging patterns of data coverage and representativeness. Best species coverage is achieved for categorical traits—almost complete coverage for ‘plant growth form’. However, most traits relevant for ecology and vegetation modelling are characterized by continuous intraspecific variation and trait–environmental relationships. These traits have to be measured on individual plants in their respective environment. Despite unprecedented data coverage, we observe a humbling lack of completeness and representativeness of these continuous traits in many aspects. We, therefore, conclude that reducing data gaps and biases in the TRY database remains a key challenge and requires a coordinated approach to data mobilization and trait measurements. This can only be achieved in collaboration with other initiatives.

6 May 2012 in Nature Climate Change
Verified
Journal Article
Closed access
SDStefan Dullinger
Stefan Dullinger
AGAndreas Gattringer
Andreas Gattringer
WTWilfried Thuiller
Wilfried Thuiller
DMDietmar Moser
Dietmar Moser
NZNiklaus Zimmermann
Niklaus Zimmermann
KHKarl Hülber
Karl Hülber

2 August 2016 in Functional Ecology
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Journal Article
Open access
PDF file
Simon PierceSimon Pierce
Simon Pierce
DNDaniel Negreiros
Daniel Negreiros
BCBruno E. L. Cerabolini
Bruno E. L. Cerabolini
JKJens Kattge
Jens Kattge
SDSandra Díaz
Sandra Díaz
DTDuccio Tampucci
Duccio Tampucci
Summary: Competitor, stress‐tolerator, ruderal (CSR) theory is a prominent plant functional strategy scheme previously applied to local floras. Globally, the wide geographic and phylogenetic coverage of available values of leaf area (LA), leaf dry matter content (LDMC) and specific leaf area (SLA) (representing, respectively, interspecific variation in plant size and conservative vs. acquisitive resource economics) promises the general application of CSR strategies across biomes, including the tropical forests hosting a large proportion of Earth's diversity. We used trait variation for 3068 tracheophytes (representing 198 families, six continents and 14 biomes) to create a globally calibrated CSR strategy calculator tool and investigate strategy–environment relationships across biomes world‐wide. Due to disparity in trait availability globally, co‐inertia analysis was used to check correspondence between a ‘wide geographic coverage, few traits’ data set and a ‘restricted coverage, many traits’ subset of 371 species for which 14 whole‐plant, flowering, seed and leaf traits (including leaf nitrogen content) were available. CSR strategy/environment relationships within biomes were investigated using fourth‐corner and RLQ analyses to determine strategy/climate specializations. Strong, significant concordance (RV = 0·597; P < 0·0001) was evident between the 14 trait multivariate space and when only LA, LDMC and SLA were used. Biomes such as tropical moist broadleaf forests exhibited strategy convergence (i.e. clustered around a CS/CSR median; C:S:R = 43:42:15%), with CS‐selection associated with warm, stable situations (lesser temperature seasonality), with greater annual precipitation and potential evapotranspiration. Other biomes were characterized by strategy divergence: for example, deserts varied between xeromorphic perennials such as Larrea divaricata, classified as S‐selected (C:S:R = 1:99:0%) and broadly R‐selected annual herbs (e.g. Claytonia perfoliata; R/CR‐selected; C:S:R = 21:0:79%). Strategy convergence was evident for several growth habits (e.g. trees) but not others (forbs). The CSR strategies of vascular plants can now be compared quantitatively within and between biomes at the global scale. Through known linkages between underlying leaf traits and growth rates, herbivory and decomposition rates, this method and the strategy–environment relationships it elucidates will help to predict which kinds of species may assemble in response to changes in biogeochemical cycles, climate and land use.

12 November 2016 in Global Change Biology
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Journal Article
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MCMaxime Cailleret
Maxime Cailleret
SJSteven Jansen
Steven Jansen
ERElisabeth M. R. Robert
Elisabeth M. R. Robert
LDLucía Desoto
Lucía Desoto
TATuomas Aakala
Tuomas Aakala
JMJordi Martínez‐Vilalta
Jordi Martínez‐Vilalta
Tree mortality is a key factor influencing forest functions and dynamics, but our understanding of the mechanisms leading to mortality and the associated changes in tree growth rates are still limited. We compiled a new pan‐continental tree‐ring width database from sites where both dead and living trees were sampled (2970 dead and 4224 living trees from 190 sites, including 36 species), and compared early and recent growth rates between trees that died and those that survived a given mortality event. We observed a decrease in radial growth before death in ca. 84% of the mortality events. The extent and duration of these reductions were highly variable (1–100 years in 96% of events) due to the complex interactions among study species and the source(s) of mortality. Strong and long‐lasting declines were found for gymnosperms, shade‐ and drought‐tolerant species, and trees that died from competition. Angiosperms and trees that died due to biotic attacks (especially bark‐beetles) typically showed relatively small and short‐term growth reductions. Our analysis did not highlight any universal trade‐off between early growth and tree longevity within a species, although this result may also reflect high variability in sampling design among sites. The intersite and interspecific variability in growth patterns before mortality provides valuable information on the nature of the mortality process, which is consistent with our understanding of the physiological mechanisms leading to mortality. Abrupt changes in growth immediately before death can be associated with generalized hydraulic failure and/or bark‐beetle attack, while long‐term decrease in growth may be associated with a gradual decline in hydraulic performance coupled with depletion in carbon reserves. Our results imply that growth‐based mortality algorithms may be a powerful tool for predicting gymnosperm mortality induced by chronic stress, but not necessarily so for angiosperms and in case of intense drought or bark‐beetle outbreaks.

25 September 2004 in Geophysical Research Letters
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Journal Article
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SPSerge Payette
Serge Payette
ADAnn Delwaide
Ann Delwaide
Marco CaccianigaMarco Caccianiga
Marco Caccianiga
MBMichel Beauchemin
Michel Beauchemin

23 July 2016 in Methods in Ecology and Evolution
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Journal Article
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CRCarlo Ricotta
Carlo Ricotta
FBFrancesco de Bello
Francesco de Bello
MMMarco Moretti
Marco Moretti
Marco CaccianigaMarco Caccianiga
Marco Caccianiga
BCBruno E.L. Cerabolini
Bruno E.L. Cerabolini
SPSandrine Pavoine
Sandrine Pavoine