Quantifying biodiversity: procedures and pitfalls in the measurement and comparison of species richness
By Nicholas Gotelli, Robert K. Colwell. 2001
6,409 citations recorded by the source corpus.
Subfields: Ecological Modeling, Ecology, Evolution, Behavior and Systematics, Nature and Landscape Conservation
View Paper: https://www.semanticscholar.org/paper/57a8ed20c0eef540bc4b3cf727c19bfd0a2dea5c
How researchers see this paper
The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.
In Ecological Modeling
- Jorge M. Lobo
- Wilfried Thuiller
- A. Chao
- Miguel B. Araújo
- Joaquín Hortal
- Robert K. Colwell
- A. Townsend Peterson
- Antoine Guisan
In Ecology, Evolution, Behavior and Systematics
- A. Chao
- Robert K. Colwell
- T. Tscharntke
- Pedro Jordano
- Carsten F. Dormann
- Chun‐Huo Chiu
- Francesco de Bello
- Hanna Tuomisto
In Nature and Landscape Conservation
- A. Chao
- Robert K. Colwell
- Wilfried Thuiller
- Jorge M. Lobo
- Nicholas Gotelli
- Francesco de Bello
- Pedro Cardoso
- Chun‐Huo Chiu
Citations in the corpus
- Psychological benefits of greenspace increase with biodiversity (2007, methodology): “Species richness estimates (species density of Gotelli & Colwell 2001) were calculated using the second-order jackknife estimator computed over 1000 runs in the ESTIMATES software (Colwell 2005).”
- Acoustic fish communities: sound diversity of rocky habitats reflects fish species diversity (2019, methodology): “Accumulation curves (using presence/absence data) were also built, allowing for meaningful comparison of community-wide changes (Gotelli & Colwell 2001, Gotelli & Chao 2013).”
- The elevational gradient in Andean bird species richness at the local scale: a foothill peak and a high‐elevation plateau (2005, methodology): “Gotelli and Colwell (2001) suggested that x-axes of sample-based rarefaction curves should be rescaled from samples to individuals because datasets may differ systematically in the number of individuals per sample.”
- Network properties of an epiphyte metacommunity (2007, methodology): “To evaluate the completeness of species-based surveys, I conducted rarefaction analyses (see Gotelli & Colwell 2001) using RAREFACT 1.0.”
- Stand composition and structure of the boreal mixedwood and epigaeic arthropods of the Ecosystem Management Emulating Natural Disturbance (EMEND) landbase in northwestern Alberta (2004, background): “Rarefaction standardizes comparisons of species richness among samples (in our case, cover types) by drawing random and incremental subsamples of individuals within samples (Gotelli and Colwell 2001).”
- Conservation status and threats for African reptiles (2016, methodology): “However, unreliable species richness patterns for African reptiles could potentially be improved through correction methods such as rarefaction or species distribution modelling (Engemann et al., 2015; Gotelli and Colwell, 2001; Jiménez et al., 2009; Mecenero et al., 2015; Raxworthy et al., 2003).”
- Marine nematode deep‐sea biodiversity – hyperdiverse or hype? (2003, background): “Again, this is consistent with Grassle & Morse-Porteus (1992) spatial–temporal mosaic hypothesis, which appears to be a plausible explanatory mechanism for the structure of deep-sea nematode assemblages.”
- Stygobiotic crustacean species richness: a question of numbers, a matter of scale (2010, methodology): “At the stygoregional, regional, and aquifer scales, sample-based rarefaction curves ( Gotelli & Colwell, 2001 ) were calculated to compare species richness across the different areas, to minimize the effect of sampling effort.”
- Biodiversity soup: metabarcoding of arthropods for rapid biodiversity assessment and biomonitoring (2012, neutral): “Rarefaction must therefore be used to control for the effects of sample size (Gotelli & Colwell 2001).”
- Diversity, distribution and spatial structure of the cold-water coral fauna of the Azores (NE Atlantic) (2013, background): “Increasing sampling areas will lead to an increased probability of encountering rare species (Gotelli and Colwell, 2001).”
- Year‐to‐year variation in the topology of a plant–pollinator interaction network (2008, background): “number of individual flower visits tallied) differs (Gotelli and Colwell 2001).”
- Imperfect detection is the rule rather than the exception in plant distribution studies (2013, background): “The collection of sites where a species occurs represents the distribution of that species (Guisan & Thuiller 2005), while the collection of species occurring at a site represents species richness, the most widely used metric of biodiversity (Gotelli & Colwell 2001).”
- Determinants of species richness in generalist and specialist Mediterranean butterflies: the negative synergistic forces of climate and habitat change (2011, background): “This simple measure has been criticised because the sample sizes are different at each site (Gotelli and Colwell 2001).”
- Seed dispersal by dabbling ducks: an overlooked dispersal pathway for a broad spectrum of plant species (2016, methodology): “Rarefaction curves were produced by repeatedly resampling a pool of n = 50 individuals at random (with repetition) and plotting the average cumulative number of seed species represented by 1, 2, . . ., n individuals as a function of the number of ducks sampled (Gotelli & Colwell 2001).”
- Significance of Specimen Databases from Taxonomic Revisions for Estimating and Mapping the Global Species Diversity of Invertebrates and Repatriating Reliable Specimen Data (2004, background): “But especially in invertebrates, relying on observed species lists “without reference to a taxon sampling-curve is problematic at best” (Gotelli & Colwell 2001).”