Richard Grenyer’s research while affiliated with University of Oxford and other places

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Publications (63)


Conceptual framework to test spatial dependence. (a) Biodiversity facets from different sites are clustered onto a 2 × 1 SOM surface. (b and c) Recognised patterns of diversity change show strong geographic structures. (d and e) Recognised patterns of diversity change have medium geographic structures. (f and g) Represent no evidence for strong or medium geographic structures underlying the recognised patterns of diversity change. An average nearest neighbour (ANN) distance is used to measure the geographic proximity of different locations. ANN distance from the diversity time‐series falling to the left of the histogram of ANN distances for randomly generated locations supports that geographic structure is important for pattern recognition (c and e), whilst ANN distance from real diversity time‐series adhering to recognition of the weak geographic pattern will fall in the middle of the distribution (g). Points in (b), (d), and (f) with the same colour surrounded by a dotted circle represent that they have similar diversity change and are recognised into the same pattern. Solid lines in (c), (e) and (g) represent the ANN distance of diversity time‐series, and dashed lines represent the average ANN distance for a set of random samples.
Distribution of survey routes in the North American Breeding Birds Survey and spatial independence test. Each panel presents the distribution of diversity time‐series that have the same pattern as identified by the SOM. The inset density plot shows the distribution of the ANN distance of 1000 Monte Carlo tests. Solid lines in the density plot represent the average nearest neighbour (ANN) distance of the survey routes, and dashed lines represent the mean value of ANN for 1000 random samples. Blue points represent the start locations of survey routes in the focal SOM group and orange points are the start locations of other survey routes that do not follow into the SOM group. Percentages on the left top of each panel denote the percentages of time‐series in that group to all time‐series. Pseudo p‐values represent the probability of incorrectness if rejecting the geographic independence hypothesis that diversity time‐series that have the same pattern are randomly distributed.
Distribution and spatial independence test of survey routes for the North American Breeding Birds Survey to the east of Mississippi River. Each panel presents the distribution of diversity time‐series that have the same pattern as identified by the SOM. The inset density plot shows the distribution of the ANN distance of 1000 Monte Carlo tests. Solid lines in the density plot represent the average nearest neighbour (ANN) distance of the survey routes, and dashed lines represent the mean value of ANN for 1000 random samples. Blue points represent the start locations of each survey route in the focal SOM group and orange points are the start locations of other survey routes that do not follow into the SOM group. Percentages in the left top of each panel denote the percentages of time‐series in that group to all time‐series. Pseudo p‐values represent the probability of incorrectness if rejecting the geographic independence hypothesis that diversity time‐series that have the same pattern are randomly distributed.
Temporal changes of taxonomic, functional and phylogenetic diversity in the North American Breeding Birds Survey. Each panel denotes the change of diversity time‐series that have the same pattern. The error bars represent a 95% confidence interval. The non‐linear regressions (a loess sliding window with a 33% range width; smoothed line) of the diversity facets were added to describe the major temporal trajectory of each group.
Distribution and spatial independence test of enhanced vegetation index (EVI) time‐series from the same locations as bird survey routes. Each panel presents the distribution of EVI time‐series (blue pixels) that have the same pattern. The inset density plot shows the distribution of the ANN distance of 1000 Monte Carlo tests. Solid lines in the density plot represent the average nearest neighbour (ANN) distance of the locations of EVI time‐series, and dashed lines represent the mean value of ANN for 1000 random samples. Blue points represent the start locations of each survey route in the focal SOM group and orange points are the start locations of other survey routes that do not follow into the SOM group. Percentages in the left top of each panel denote the percentages of time‐series in that group to all time‐series. Pseudo p‐values represent the probability of incorrectness if rejecting the geographic independence hypothesis that EVI time‐series that have the same pattern are randomly distributed.
Challenging the geographic bias in recognising large‐scale patterns of diversity change
  • Article
  • Full-text available

September 2023

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259 Reads

Wenyuan Zhang

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Richard Grenyer

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Ben C. Sheldon

Aim Geographic structure is a fundamental organising principle in ecological and Earth sciences, and our planet is conceptually divided into distinct geographic clusters (e.g. ecoregions and biomes) demarcating unique diversity patterns. Given recent advances in technology and data availability, however, we ask whether geographically clustering diversity time‐series should be the default framework to identify meaningful patterns of diversity change. Location North America. Taxon Aves. Methods We first propose a framework that recognises patterns of diversity change based on similarities in the behaviour of diversity time‐series, independent of their specific or relative spatial locations. Specifically, we applied an artificial neural network approach, the self‐organising map (SOM), to group time‐series of over 0.9 million observations from the North American Breeding Birds Survey (BBS) data from 1973 to 2016. We then test whether time‐series identified as having similar behaviour are geographically structured. Results We find little evidence of strong geographic structure in patterns of diversity change for North American breeding birds. The majority of the recognised diversity time‐series patterns tend to be indistinguishable from being independently distributed in space. Main Conclusions Our results suggest that geographic proximity may not correspond to shared temporal trends in diversity; assuming that geographic clustering is the basis for analysis may bias diversity trend estimation. We suggest that approaches that consider variability independently of geographic structure can serve as a useful addition to existing organising rules of biodiversity time‐series.

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Automated assessment reveals that the extinction risk of reptiles is widely underestimated across space and phylogeny

May 2022

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862 Reads

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63 Citations

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Richard Grenyer

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The Red List of Threatened Species, published by the International Union for Conservation of Nature (IUCN), is a crucial tool for conservation decision-making. However, despite substantial effort, numerous species remain unassessed or have insufficient data available to be assigned a Red List extinction risk category. Moreover, the Red Listing process is subject to various sources of uncertainty and bias. The development of robust automated assessment methods could serve as an efficient and highly useful tool to accelerate the assessment process and offer provisional assessments. Here, we aimed to (1) present a machine learning–based automated extinction risk assessment method that can be used on less known species; (2) offer provisional assessments for all reptiles—the only major tetrapod group without a comprehensive Red List assessment; and (3) evaluate potential effects of human decision biases on the outcome of assessments. We use the method presented here to assess 4,369 reptile species that are currently unassessed or classified as Data Deficient by the IUCN. The models used in our predictions were 90% accurate in classifying species as threatened/nonthreatened, and 84% accurate in predicting specific extinction risk categories. Unassessed and Data Deficient reptiles were considerably more likely to be threatened than assessed species, adding to mounting evidence that these species warrant more conservation attention. The overall proportion of threatened species greatly increased when we included our provisional assessments. Assessor identities strongly affected prediction outcomes, suggesting that assessor effects need to be carefully considered in extinction risk assessments. Regions and taxa we identified as likely to be more threatened should be given increased attention in new assessments and conservation planning. Lastly, the method we present here can be easily implemented to help bridge the assessment gap for other less known taxa.


Automated assessment reveals extinction risk of reptiles is widely underestimated across space and phylogeny

January 2022

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256 Reads

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1 Citation

The Red List of Threatened Species, published by the International Union for Conservation of Nature (IUCN), is a crucial tool for conservation decision making. However, despite substantial effort, numerous species remain unassessed, or have insufficient data available to be assigned a Red List threat category. Moreover, the Red Listing process is subject to various sources of uncertainty and bias. The development of robust automated assessment methods could serve as an efficient and highly useful tool to accelerate the assessment process and offer provisional assessments. Here we aimed to: 1) present a machine learning based automated threat assessment method that can be used on less known species; 2) offer provisional assessments for all reptiles - the only major tetrapod group without a comprehensive Red List assessment; and 3) evaluate potential effects of human decision biases on the outcome of assessments . We use the method presented here to assess 4,369 reptile species that are currently unassessed or classified as Data Deficient by the IUCN. Our models range in accuracy from 88% to 93% for classifying species as threatened/non-threatened, and from 82% to 87% for predicting specific threat categories. Unassessed and Data Deficient reptiles were more likely to be threatened than assessed species, adding to mounting evidence that they should be considered threatened by default. The overall proportion of threatened species greatly increased when we included our provisional assessments. Assessor identities strongly affected prediction outcomes, suggesting that assessor effects need to be carefully considered in extinction risk assessments. Regions and taxa we identified as likely to be more threatened should be given increased attention in new assessments and conservation planning. Lastly, the method we present here can be easily implemented to help bridge the assessment gap on other less known taxa.


Habitat change and biased sampling influence estimation of diversity trends

June 2021

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156 Reads

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18 Citations

Current Biology

Recent studies have drawn contrasting conclusions about the extent to which local-scale measures of biodiversity are declining and whether such patterns conflict with the global-scale declines that have attracted much attention.¹ A key source of high-quality data for such analyses comes from longitudinal biodiversity studies, which sample a given taxon repeatedly over time at a specific location.² There has been relatively little consideration of how habitat change might lead to biases in the sampling and continuity of biodiversity time series data, and the consequent potential for bias in the biodiversity trends that result. Here, based on analysis of standardized routes from the North American Breeding Bird Survey (3,014 routes sampled over 18 years),³ we demonstrate that major local habitat change is associated with an increase in the rate of survey cessations. We further show that routes that were continued despite major habitat changes show reduced diversity. By simulating potential rates of loss, we show that the underlying real trends in taxonomic, functional, and phylogenetic diversity can even reverse in sign if more than a quarter of diversity is lost from routes that ceased and are thus no longer included in surveys. Our analyses imply that biodiversity loss can be underestimated by biases introduced if continued sampling in longitudinal studies is influenced by local change. We argue that researchers and conservation practitioners should be aware of the potential for bias in such data and seek to use more robust methods to evaluate biodiversity trends and make conservation decisions.


Fig. 3 Global patterns of reptilian phylogenetic endemism (PE) and human pressure. a regions of high reptilian PE (richest 10% of grid cells) and the level of human pressure in each grid cell. b Global patterns of reptilian human-impacted phylogenetic endemism (HIPE), where grid cells are coloured by the cumulative amount of global HIPE captured; darkest red cells comprise the highest-scoring grid cells which together capture 10% of global HIPE, whereas the lowest-scoring grid cells which together capture 10% of global HIPE are coloured dark blue. c ratio of HIPE to PE for grid cells under very high human pressure (HF ≥ 12). Given that we only show cells of very high human pressure, a ratio of 1:1 (darkest red) means all PD found in the grid cell is restricted to regions of very high human pressure, and the lower this becomes (increasingly lighter reds), the greater the proportion of phylogenetic diversity also distributed in regions with less human pressure.
Fig. 4 Global patterns of tetrapod human-impacted phylogenetic endemism (HIPE) and reptilian contributions. The global patterns of (a) the proportion of tetrapod HIPE contributed by reptiles (from 100% of HIPE contributed by reptiles in black to 0% of HIPE in light grey); and (b) tetrapod HIPE, where grid cells are coloured by the cumulative amount of global HIPE captured; darkest red cells comprise the highest-scoring grid cells which together capture 10% of global HIPE, whereas the lowestscoring grid cells which together capture 10% of global HIPE are coloured dark blue.
Relationships between spatial and species-level phylogenetic diversity-based metrics
Flowchart illustrating the data sources used, stages of processing, and relationships between the spatial and species-level metrics used here. Metrics are in red boxes, data sources in black, and processing stages in blue. Only those metrics for which results are reported and presented in the main text are included. Our three novel metrics are denoted with asterisks. Mathematical definitions for all spatial and species-level metrics are discussed in Supplementary Table 1.
Global patterns of reptilian phylogenetic diversity (PD)
Cumulative PD, in millions of years (MY) (left), Middle: residual PD per grid cell, in MY, (warm colours: more than expected given richness, cold colours: less than expected given richness), Right: the relationship between richness and PD across all grid cells from the middle panels for lizards (a–c), snakes (d–f), and turtles (g–i), with colours corresponding to the grid cell values from the middle panels.
Distributions of human-impacted terminal endemism (HITE) for tetrapods
a Density distributions of log-transformed HITE scores for tetrapods. Species with long terminal branches occurring in very few grid cells under high human pressure score highly and fall on the right of the x-axis, whereas species with short terminal branches and large ranges encompassing regions of low human pressure fall on the left of the x-axis. Y-axis indicates density of species in each clade with a given HITE value. b Distribution of HITE scores (in 10⁻³ MY⁻¹ km²) across tetrapods for each IUCN Red List category (excluding Extinct, Extinct in the Wild and unassessed species): Data Deficient (DD; n = 2604 spp., grey box); Least Concern (LC; n = 15217 spp., dark green box); Near Threatened (NT; n = 1709 spp., light green box); Vulnerable (VU; n = 2007 spp., yellow box); Endangered (EN; n = 1965 spp., orange box); Critically Endangered (CR; n = 1035 spp., red box). c Distribution of HITE scores (in 10⁻³ MY⁻¹ km²) for Data Deficient (DD) tetrapod species for key tetrapod groups, from left to right on x-axis: lizards (n = 478 DD spp.), snakes (n = 404), turtles (n = 8), amphibians (n = 1222), birds (n = 35) and mammals (n = 457). For boxplots, centre line = median; box limits = upper and lower quartiles; whiskers = 1.5x interquartile range. Source data are provided as a Source Data file.
Global priorities for conservation of reptilian phylogenetic diversity in the face of human impacts

May 2020

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1,125 Reads

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80 Citations

Phylogenetic diversity measures are increasingly used in conservation planning to represent aspects of biodiversity beyond that captured by species richness. Here we develop two new metrics that combine phylogenetic diversity and the extent of human pressure across the spatial distribution of species-one metric valuing regions and another prioritising species. We evaluate these metrics for reptiles, which have been largely neglected in previous studies, and contrast these results with equivalent calculations for all terrestrial vertebrate groups. We find that regions under high human pressure coincide with the most irreplaceable areas of reptilian diversity, and more than expected by chance. The highest priority reptile species score far above the top mammal and bird species, and reptiles include a disproportionate number of species with insufficient extinction risk data. Data Deficient species are, in terms of our species-level metric, comparable to Critically Endangered species and therefore may require urgent conservation attention.


Results from the place-only, integrated, and random approaches.
Performance comparisons across scenarios
The scenario performance of the place-only, integrated, and random approaches (a−h) in achieving biodiversity representation (defined as the number of background species protected). Random selections were performed 100 times for each scenario. Threat status refers to the candidate flagship group subset by IUCN classification of Near-Threatened and higher. Source data are provided in the Source Data file.
Visualization of prioritized places and candidate flagship species
The map shows the 47 places and a sample of the candidate flagship species (panels A–I) delivered from the integrated approach for Scenario h (Fig. 1h, Table 2). See Supplementary Data Table 2 for full list of species. See Supplementary Table 3 for associated places and ecoregions.
Conservation prioritization can resolve the flagship species conundrum

February 2020

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935 Reads

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108 Citations

Conservation strategies based on charismatic flagship species, such as tigers, lions, and elephants, successfully attract funding from individuals and corporate donors. However, critics of this species-focused approach argue it wastes resources and often does not benefit broader biodiversity. If true, then the best way of raising conservation funds excludes the best way of spending it. Here we show that this conundrum can be resolved, and that the flagship species approach does not impede cost-effective conservation. Through a tailored prioritization approach, we identify places containing flagship species while also maximizing global biodiversity representation (based on 19,616 terrestrial and freshwater species). We then compare these results to scenarios that only maximized biodiversity representation, and demonstrate that our flagship-based approach achieves 79−89% of our objective. This provides strong evidence that prudently selected flagships can both raise funds for conservation and help target where these resources are best spent to conserve biodiversity. Conservation actions focused on flagship species are effective at raising funds and awareness. Here, McGowan et al. show that prioritizing areas for conservation based on the presence of flagship species results in the selection of areas with ~ 79-89% of the total species that would be selected by maximizing biodiversity representation only.


Classification and ordination of the main plant communities of the Eastern Hajar Mountains, Oman

October 2019

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73 Reads

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9 Citations

Journal of Arid Environments

This article presents a quantitative description of the plant communities of the Eastern Hajar Mountains of Oman and the primary environmental variables affecting their composition and distribution. Species inventories and environmental data were collected from 110 vegetation plots covering elevation from 1000 m to the highest point in the mountains at about 2200 m. Measurements of 12 environmental variables were used in the analysis: aspect, slope, annual rainfall, soil pH, salinity, soil nutrients (N, P, K, Ca) and soil texture (clay and silt). Two Way Indicator Species Analysis (TWINSPAN) classification, Detrended Correspondence Analysis (DCA) and Canonical Correspondence Analysis (CCA) ordinations showed four well-distinguished plant communities. Although some species overlap occurred in the transition zones between the communities, these plant communities were characteristic for their zones. Annual rainfall, total nitrogen and total calcium were the most important environmental factors affecting the distribution of plant communities. The high-altitude community was always distinctly identified using all different data treatments, while the lower-altitude communities tended mostly to overlap. Any grazing effect on plant community distribution appears to be overridden by the other environmental variables.


Figure 1: Global patterns of reptilian phylogenetic diversity (PD). Cumulative PD, in millions of years 300
Figure 2: Reptilian Phylogenetic Endemism (PE) and Human Footprint (HF). a) The global relationship 321
Figure 3: Global patterns of tetrapod HIPE and reptilian contributions. The global patterns of a) the 353
Figure 4: Distributions of Human Impacted Terminal Endemism (HITE) for tetrapods. a) Density 382
Global priorities for conservation of reptilian phylogenetic diversity in the face of human impacts

August 2019

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1,479 Reads

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1 Citation

Phylogenetic Diversity (PD) is increasingly recognised as an important measure that can provide information on evolutionary and functional aspects of biodiversity for conservation planning that are not readily captured by species diversity. Here we develop and analyse two new metrics that combine the effects of PD and human encroachment on species range size - one metric valuing regions and another enabling species prioritisation. We evaluate these metrics for reptiles, which have been largely neglected in previous studies, and contrast these results with equivalent calculations for all terrestrial vertebrate groups. We find that high human impacted areas unfortunately coincide with the most valuable areas of reptilian diversity, more than expected by chance. We also find that, under our species-level metric, the highest priority reptile species score far above the top mammal and bird species, and they include a disproportionate number of species with insufficient information on potential threats. Such Data Deficient species are, in terms of our metric, comparable to Critically Endangered species and may require urgent conservation attention.


Fig. 2. Comparing measures of phylogenetic diversity (PD). Faith's phylogenetic diversity (PD Faith ) is the sum of the branch lengths on the minimum spanning tree linking a set of terminal taxa to the root. This inclusion of an unnamed root taxon results in an implicit complementarity aspect to PD Faith . Not all definitions of PD include the root, which avoids this complementarity issue, but has created a source of confusion in the literature. Values indicate branch lengths -note here that the tips are all not the same distance from the root; species are identified with letters shown at tips. PD Faith for sets (A,B) and (C,D) would be 7. A PD measure that sums just the branch lengths on the minimum spanning tree would lead to a value of 1 + 1 = 2 for the (A,B) subset and 2 + 2 = 4 for the (C,D) subset.
Summary table reflecting the logic, support for or against, and future directions for each argument regarding the human-centric benefits of evolutionary history
Assessing the Utility of Conserving Evolutionary History

May 2019

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5,771 Reads

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97 Citations

Biological reviews of the Cambridge Philosophical Society

It is often claimed that conserving evolutionary history is more efficient than species‐based approaches for capturing the attributes of biodiversity that benefit people. This claim underpins academic analyses and recommendations about the distribution and prioritization of species and areas for conservation, but evolutionary history is rarely considered in practical conservation activities. One impediment to implementation is that arguments related to the human‐centric benefits of evolutionary history are often vague and the underlying mechanisms poorly explored. Herein we identify the arguments linking the prioritization of evolutionary history with benefits to people, and for each we explicate the purported mechanism, and evaluate its theoretical and empirical support. We find that, even after 25 years of academic research, the strength of evidence linking evolutionary history to human benefits is still fragile. Most – but not all – arguments rely on the assumption that evolutionary history is a useful surrogate for phenotypic diversity. This surrogacy relationship in turn underlies additional arguments, particularly that, by capturing more phenotypic diversity, evolutionary history will preserve greater ecosystem functioning, capture more of the natural variety that humans prefer, and allow the maintenance of future benefits to humans. A surrogate relationship between evolutionary history and phenotypic diversity appears reasonable given theoretical and empirical results, but the strength of this relationship varies greatly. To the extent that evolutionary history captures unmeasured phenotypic diversity, maximizing the representation of evolutionary history should capture variation in species characteristics that are otherwise unknown, supporting some of the existing arguments. However, there is great variation in the strength and availability of evidence for benefits associated with protecting phenotypic diversity. There are many studies finding positive biodiversity–ecosystem functioning relationships, but little work exists on the maintenance of future benefits or the degree to which humans prefer sets of species with high phenotypic diversity or evolutionary history. Although several arguments link the protection of evolutionary history directly with the reduction of extinction rates, and with the production of relatively greater future biodiversity via increased adaptation or diversification, there are few direct tests. Several of these putative benefits have mismatches between the relevant spatial scales for conservation actions and the spatial scales at which benefits to humans are realized. It will be important for future work to fill in some of these gaps through direct tests of the arguments we define here.



Citations (48)


... Owing to the ease of collection from preserved museum samples, we primarily focused our study RESEARCH | RESEARCH ARTICLE on the external ear, a distinguishing feature of most extant mammals, with its earliest paleontological evidence dating to the Early Cretaceous, 125 million years ago (28). We examined ear cartilage from a total of 65 species, covering 4 orders of marsupials and 18 orders of eutherians, and found lipocartilage in multiple species across the clade (Fig. 6A and table S9) (29). ...

Reference:

Superstable lipid vacuoles endow cartilage with its shape and biomechanics
The delayed rise of present-day mammals

Nature

... These findings emphasize the conservation significance of many DD species that are at risk of extinction but remain unclassified as EN by the IUCN (de Oliveira Caetano et al., 2022). Enhanced and precise evaluations of unregistered or DD species are vital for refining conservation priorities and ensuring their inclusion in sustainable development goals and biodiversity preservation. ...

Automated assessment reveals that the extinction risk of reptiles is widely underestimated across space and phylogeny

... We coded species as limbless and as limb-reduced according to the F I G U R E 2 World maps showing the distribution and richness of (a) fully limbed skink species and (b) limb-reduced and limbless skink species. Richness and distribution data modelled after de Oliveira Caetano et al. (2022). definition used for our dataset. ...

Automated assessment reveals extinction risk of reptiles is widely underestimated across space and phylogeny

... Further, the BBS survey was not initially designed in a fully structured way and as such there are potentially problematic links between survey period and ecological predictors. For example, earlier-starting transects with longer data spans tend to be in relatively more human-modified areas, while recent heavy land use change is associated with early stopping of transect data collection (Zhang et al., 2021). ...

Habitat change and biased sampling influence estimation of diversity trends
  • Citing Article
  • June 2021

Current Biology

... This pattern was related to phylogeny, with the results showing a moderate phylogenetic signal. This is supported by various studies that found extinction risk is correlated with phylogeny (Purvis et al. 2005;Sjöström and Gross 2006;Willis et al. 2008;Fritz and Purvis 2010). ...

Correlates of extinction risk: phylogeny, biology, threat and scale
  • Citing Chapter
  • January 2001

... The IUCN Red List of Threatened Species [10] played an important role in this development, as the datasets compiled through species' assessments (maps, habitat preferences and species' categories of extinction risk) underpin a substantial fraction of the studies in this new field (e.g. [26,[45][46][47][48][49]). Datasets covering entire taxonomic groups made it possible to map global patterns of functional and phylogenetic diversity, and these patterns have in turn been used in a growing number of studies as the basis of recommendations for large-scale conservation priorities (e.g. ...

Global priorities for conservation of reptilian phylogenetic diversity in the face of human impacts

... One way to determine spatial and temporal trends and links in carbon and biodiversity is to look for biota that may serve as effective indicators of certain elements of forest habitat (e.g., intactness) as well as biodiversity (e.g., species richness) [10]). Among these biota, great apes could be particularly useful indicators, given their potential to reflect forest quality [11][12][13]. They may serve as umbrella species whose presence indirectly benefits other wild species thanks to the conservation efforts made to protect their habitats [2,14]. ...

Conservation prioritization can resolve the flagship species conundrum

... Qin et al. (2011) found a peak-shaped distribution of species diversity with increasing altitude in the Taibai Mountains, China. Harthy and Grenyer (2019) showed a single-peaked relationship between species richness and diversity with altitude in the Oman East Hajar Mountains. However, some research results indicated a negative correlation between species diversity and elevation gradient (Masviken et al., 2020;Rawal et al., 2018). ...

Classification and ordination of the main plant communities of the Eastern Hajar Mountains, Oman
  • Citing Article
  • October 2019

Journal of Arid Environments

... Traditionally, conservation strategies for quantifying biodiversity have focused on species richness and patterns of endemism (Noguera-Urbano, 2017;Winter et al., 2013;Voskamp et al., 2017;Rosauer et al., 2017). Regardless, it has become more accepted that species richness alone does not appropriately describe the spatial and temporal dynamics of biodiversity, since it only represents the taxonomic dimension of biodiversity (Safi et al., 2011;Voskamp et al., 2017;Karanth et al., 2019;Grumbs et al., 2019). In response to this challenge, other approaches for measuring biodiversity, such as phylogenetic diversity, are increasingly recognized as important components of conservation planning. ...

Global priorities for conservation of reptilian phylogenetic diversity in the face of human impacts

... As evolution shapes species traits, phylogenetic approaches can efficiently capture highdimensional ecological differences, reducing the risks of omitting important traits (Tucker et al. 2017. Additionally, phylogenetic diversity has exhibited similar or even better performance than taxonomic diversity in explaining ecosystem functions or services across sites (Tucker et al. 2019; van der Plas 2019). ...

Assessing the Utility of Conserving Evolutionary History

Biological reviews of the Cambridge Philosophical Society