Overyielding among plant functional groups in a long‐term experiment
By David U Hooper, J. Dukes. 2003
345 citations recorded by the source corpus.
Subfields: Ecology, Ecology, Evolution, Behavior and Systematics, Nature and Landscape Conservation
View Paper: https://www.semanticscholar.org/paper/6804e07a679f52632c1913df8e18f859784ef02d
How researchers see this paper
The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.
In Ecology
- Barbara C. Schmid
- J. Emmett Duffy
- J. Bruno
- J. Dukes
- J. Fox
- David U Hooper
- M. Scherer‐Lorenzen
- Michel Loreau
In Ecology, Evolution, Behavior and Systematics
- Barbara C. Schmid
- S. Lavorel
- David A. Wardle
- J. Emmett Duffy
- T. Tscharntke
- Michel Loreau
- J. Dukes
- J. Tylianakis
In Nature and Landscape Conservation
- S. Lavorel
- Barbara C. Schmid
- David A. Wardle
- M. Scherer‐Lorenzen
- J. Emmett Duffy
- Michel Loreau
- Francesco de Bello
- Peter B. Reich
Citations in the corpus
- Contrasting mass‐ratio vs. niche complementarity effects on litter C and N loss during decomposition along a regional climatic gradient (2017, background): “…complementarity’ hypothesis argues that it is the degree of trait variation within a community that matters most, as higher complementarity in resource use between species may promote a more efficient acquisition of resources, and hence higher productivity (Hooper & Dukes 2004; D ıaz et al. 2007).”
- No evidence of spatial root system segregation and elevated fine root biomass in multi-species temperate broad-leaved forests (2009, background): “This is all the more interesting since some authors have emphasized that diversity effects such as overyielding might be caused more by functional properties of particular species rather than by species richness per se (Hooper and Vitousek 1997; Hooper and Dukes 2004).”
- Biodiversity and ecosystem functioning: reconciling the results of experimental and observational studies (2007, result): “While we could only maintain weeded communities at all sites for 3 years (but for up to eight at some) patterns were generally weakest in the first year and strengthened or maintained thereafter (Pfisterer et al. 2004; Spehn et al. 2005), as were those from comparable studies (Tilman et al. 2001; H”
- Long‐term enhancement of agricultural production by restoration of biodiversity (2006, background): “Other studies that have extended beyond 3 years have found a maintained effect of species richness on productivity (HilleRisLambers et al. 2004; Hooper & Dukes 2004; Hofmann & Isselstein 2005; Schlapfer, Pfisterer & Schmid 2005; van Ruijven & Berendse 2005) and some have even shown an increase in th”
- Partitioning the effects of algal species identity and richness on benthic marine primary production (2006, background): “…the effects of plant richness on primary production are modest and sometimes undetectable, often because highly productive species fail to dominate diverse plant assemblages (Loreau and Hector 2001, Fridley 2002, Hector et al. 2002, Callaway et al. 2003, Hooper and Dukes 2004, Bruno et al. 2005).”
- Overyielding in experimental grassland communities - irrespective of species pool or spatial scale (2005, background): “…as primary mechanisms behind overyielding accompanied by varying contributions of selection effects ranging from predominantly negative (e.g. van Ruijven & Berendse 2003; Hooper & Dukes 2004) to positive (e.g. Dimitrakopoulos & Schmid 2004) or being of minor importance (Loreau & Hector 2001).”
- New multidimensional functional diversity indices for a multifaceted framework in functional ecology. (2008, background): “…demonstrating that functional diversity, rather than species diversity, enhances ecosystem functions such as productivity (Tilman et al. 1997, Hooper and Dukes 2004, Petchey et al. 2004, Hooper et al. 2005), resilience to perturbations or invasion (Dukes 2001, Bellwood et al. 2004), and…”
- Functional Diversity — at the Crossroads between Ecosystem Functioning and Environmental Filters (2007, background): “For example, Hooper and Dukes (2004), using synthetic serpentine-grassland communities, found that functional trait differences among species lead to strong complementarity in resource use among plants, but these were not sufficient to cause consistent increases in community productivity with…”
- Complementary nitrogen use among potentially dominant species in a biodiversity experiment varies between two years (2008, background): “The occurrence of a positive relationship between species richness and biomass production has been attributed to species combinations with particular functional characteristics of the species involved or certain environmental conditions (Hooper & Dukes 2004).”