Potential Consequences of Regional Species Loss for Global Species Richness: A Quantitative Approach for Estimating Global Extinction Probabilities

2019 ◽  
Vol 53 (9) ◽  
pp. 4728-4738 ◽  
Author(s):  
Koen J. J. Kuipers ◽  
Stefanie Hellweg ◽  
Francesca Verones
Keyword(s):  
Species Richness ◽  
Quantitative Approach ◽  
Species Loss ◽  
Extinction Probabilities ◽  
Global Extinction

scholarly journals Altitudinal Vascular Plant Richness and Climate Change in the Alpine Zone of the Lefka Ori, Crete

Diversity ◽  
2021 ◽  
Vol 13 (1) ◽  
pp. 22
Author(s):  
George Kazakis ◽  
Dany Ghosn ◽  
Ilektra Remoundou ◽  
Panagiotis Nyktas ◽  
Michael A. Talias ◽  
...  
Keyword(s):  
Climate Change ◽  
Species Richness ◽  
Spatial Scales ◽  
Vascular Plant ◽  
Monitoring Network ◽  
Mediterranean Area ◽  
Mean Annual Temperature ◽  
High Mountain ◽  
Species Loss ◽  
Total Species Richness

High mountain zones in the Mediterranean area are considered more vulnerable in comparison to lower altitudes zones. Lefka Ori massif, a global biodiversity hotspot on the island of Crete is part of the Global Observation Research Initiative in Alpine Environments (GLORIA) monitoring network. The paper examines species and vegetation changes with respect to climate and altitude over a seven-year period (2001–2008) at a range of spatial scales (10 m Summit Area Section-SAS, 5 m SAS, 1 m2) using the GLORIA protocol in a re-survey of four mountain summits (1664 m–2339 m). The absolute species loss between 2001–2008 was 4, among which were 2 endemics. At the scale of individual summits, the highest changes were recorded at the lower summits with absolute species loss 4 in both cases. Paired t-tests for the total species richness at 1 m2 between 2001–2008, showed no significant differences. No significant differences were found at the individual summit level neither at the 5 m SAS or the 10 m SAS. Time series analysis reveals that soil mean annual temperature is increasing at all summits. Linear regressions with the climatic variables show a positive effect on species richness at the 5 m and 10 m SAS as well as species changes at the 5 m SAS. In particular, June mean temperature has the highest predictive power for species changes at the 5 m SAS. Recorded changes in species richness point more towards fluctuations within a plant community’s normal range, although there seem to be more significant diversity changes in higher summits related to aspects. Our work provides additional evidence to assess the effects of climate change on plant diversity in Mediterranean mountains and particularly those of islands which remain understudied.

scholarly journals Disruption of metal ion homeostasis in soils is associated with nitrogen deposition-induced species loss in an Inner Mongolia steppe

2015 ◽  
Vol 12 (11) ◽  
pp. 3499-3512 ◽  
Author(s):  
Q.-Y. Tian ◽  
N.-N. Liu ◽  
W.-M. Bai ◽  
L.-H. Li ◽  
W.-H. Zhang
Keyword(s):  
Species Richness ◽  
Inner Mongolia ◽  
Metal Ion ◽  
Ion Homeostasis ◽  
Base Cations ◽  
N Deposition ◽  
Species Loss ◽  
N Addition ◽  
Metal Ion Homeostasis ◽  
Addition Rate

Abstract. Enhanced deposition of atmospheric nitrogen (N) resulting from anthropogenic activities has negative impacts on plant diversity in ecosystems. Several mechanisms have been proposed to explain the species loss. Ion toxicity due to N deposition-induced soil acidification has been suggested to be responsible for species loss in acidic grasslands, while few studies have evaluated the role of soil-mediated homeostasis of ions in species loss under elevated N deposition in grasslands with neutral or alkaline soils. To determine whether soil-mediated processes are involved in changes in biodiversity induced by N deposition, the effects of 9-year N addition on soil properties, aboveground biomass (AGB) and species richness were investigated in an Inner Mongolia steppe. Low to moderate N addition rate (2, 4, 8 g N m−2 yr−1) significantly enhanced AGB of graminoids, while high N addition rate (≥ 16 g N m−2 yr−1) reduced AGB of forbs, leading to an overall increase in AGB of the community under low to moderate N addition rates. Forb richness was significantly reduced by N addition at rates greater than 8 g N m−2 yr−1, while no effect of N addition on graminoid richness was observed, resulting in decline in total species richness. N addition reduced soil pH, depleted base cations (Ca2+, Mg2+ and K+) and mobilized Mn2+, Fe3+, Cu2+ and Al3+ ions in soils. Soil inorganic-N concentration was negatively correlated with forb richness and biomass, explaining 23.59% variation of forb biomass. The concentrations of base cations (Ca2+ and Mg2+) and metal ions (Mn2+, Cu2+ and, Fe3+) showed positively and negatively linear correlation with forb richness, respectively. Changes in the metal ion concentrations accounted for 42.77% variation of forb richness, while reduction of base cations was not associated with the reduction in forb richness. These results reveal that patterns of plant biodiversity in the temperate steppe of Inner Mongolia are primarily driven by increases in metal ion availability, particularly enhanced release of soil Mn2+.

Latitudinal gradients in North American avian species richness, turnover rates and extinction probabilities

Ecography ◽  
2013 ◽  
Vol 37 (7) ◽  
pp. 626-636 ◽  
Author(s):  
Krithi K. Karanth ◽  
James D. Nichols ◽  
John R. Sauer ◽  
James E. Hines ◽  
Charles B. Yackulic
Keyword(s):  
Species Richness ◽  
North American ◽  
Avian Species ◽  
Latitudinal Gradients ◽  
Turnover Rates ◽  
Extinction Probabilities

scholarly journals Trophic structure stability and extinction dynamics of beetles (Coleoptera) in tropical forest fragments

1998 ◽  
Vol 353 (1367) ◽  
pp. 437-451 ◽  
Author(s):  
R. K. Didham ◽  
J. H. Lawton ◽  
P. M. Hammond ◽  
P. Eggleton
Keyword(s):  
Species Richness ◽  
Species Composition ◽  
Tropical Forest ◽  
Forest Fragmentation ◽  
Trophic Structure ◽  
Forest Edge ◽  
Forest Fragments ◽  
Trophic Groups ◽  
Predator Species ◽  
Extinction Probabilities

A first analysis of the stability of trophic structure following tropical forest fragmentation was performed in an experimentally fragmented tropical forest landscape in Central Amazonia. A taxonomically and trophically diverse assemblage of 993 species of beetles was sampled from 920 m 2 of leaf litter at 46 sites varying in distance from forest edge and fragment area. Beetle density increased significantly towards the forest edge and showed non-linear changes with fragment area, due to the influx of numerous disturbed-area species into 10 ha and 1 ha fragments. There was a marked change in species composition with both decreasing distance from forest edge and decreasing fragment area, but surprisingly this change in composition was not accompanied by a change in species richness. Rarefied species richness did not vary significantly across any of the sites, indicating that local extinctions of deep forest species were balanced by equivalent colonization rates of disturbed-area species. The change in species composition with fragmentation was non-random across trophic groups. Proportions of predator species and xylophage species changed significantly with distance from forest edge, but no area-dependent changes in proportions of species in trophic groups were observed. Trophic structure was also analysed with respect to proportions of abundance in six trophic groups. Proportions of abundance of all trophic groups except xylomycetophages changed markedly with respect to both distance from forest edge and fragment area. Local extinction probabilities calculated for individual beetle species supported theoretical predictions of the differential susceptibility of higher trophic levels to extinction, and of changes in trophic structure following forest fragmentation. To reduce random effects due to sampling error, only abundant species ( n ≥ 46) were analysed for extinction probabilities, as defined by absence from samples. Of these common species, 27% had significantly higher probabilities of local extinction following fragmentation. The majority of these species were predators; 42% of all abundant predator species were significantly more likely to be absent from samples in forest fragments than in undisturbed forest. These figures are regarded as minimum estimates for the entire beetle assemblage because rarer species will inevitably have higher extinction probabilities. Absolute loss of biodiversity will affect ecosystem process rates, but the differential loss of species from trophic groups will have an even greater destabilizing effect on food web structure and ecosystem function.

scholarly journals Would conserving natural land cover in landscapes conserve biodiversity?

2018 ◽  
Author(s):  
Rafael X. De Camargo ◽  
David J. Currie
Keyword(s):  
New York ◽  
Species Richness ◽  
Land Cover ◽  
Habitat Loss ◽  
New York State ◽  
Avian Species ◽  
Distribution Data ◽  
Species Loss ◽  
York State ◽  
Natural Land

ABSTRACTIt is generally accepted that protecting natural land cover would protect biodiversity. This would only be true as a general statement if the relationship between richness and natural land cover were monotonic positive and scale- and method-independent. Assertions about habitat loss causing species losses often come from broad-scale assessment of richness (e.g., from range maps) combined with patterns of natural habitat conversion. Yet, the evidence about species loss following habitat loss or fragmentation typically comes from fine-scale experiments. Here, we test whether broad-extent relationships between avian species richness and natural land cover are independent of: 1) whether species distribution data come from systematic censuses (atlases) versus range maps, and 2) the grain size of the analysis. We regressed census-based and range map-based avian species richness against the proportion of natural land cover and temperature. Censused richness at the landscape level was obtained from Breeding Bird Atlases of Ontario and New York State. Range-map richness derived from BirdLife International range maps. Comparisons were made across different spatial grains: 25-km2, 100-km2, and 900-km2. Over regional extents, range-map richness relates strongly to temperature, irrespective of spatial grain. Censused species richness relates to temperature less strongly. Range-map richness is a negative function of the proportion of natural land cover, while realized richness is a peaked function. The two measures of richness are not monotonically related to each other. In conclusion, the data do not indicate that, in practice, landscapes with greater natural land cover in southern Ontario or in New York State have higher species richness. Moreover, different data types can lead to dramatically different relationships between richness and natural land cover. We argue that the argument that habitat loss is the main driver of species loss has become a panchreston. It may be misguiding conservation biology strategies by focusing on a threat that is too general to be usefully predictive.

Species Richness and Diversity in Bee Assemblages in a Fragment of Savanna (Cerrado) at Northeastern Brazil

Sociobiology ◽  
2018 ◽  
Vol 65 (4) ◽  
pp. 566 ◽  
Author(s):  
Cândida Maria Lima Aguiar ◽  
Edson Braz Santana ◽  
Celso Feitosa Martins ◽  
Felipe Vivallo ◽  
Cláudia Oliveira Santos ◽  
...  
Keyword(s):  
Species Richness ◽  
National Park ◽  
Sampling Time ◽  
Northeastern Brazil ◽  
Sampling Effort ◽  
Species Loss ◽  
Chapada Diamantina ◽  
Factors Affecting ◽  
Ordination Analysis ◽  
Species Richness And Abundance

The conservation of the fauna of bees inhabiting the Brazilian savanna is threatened due to changes in land use in the last decades. We investigated the composition, species richness and abundance of a bee assemblage in the vicinity of the Chapada Diamantina National Park. In addition, we compiled data on composition and diversity from another bee assemblage located in the same portion of the Cerrado, which was previously investigated by one of us almost 30 years ago, in order to produce a more complete panorama on beta diversity of bees in this region. We used a non-metric multidimensional scaling ordination analysis (NMDS) to compare composition of bee assemblages from diff erent types of open vegetation. We recorded 77 bee species (H’ = 2.95; J = 0.68), 42% of them were singletons. We collected slightly more than half of the species and 60% of the genera recorded in the bee assemblage studied three decades ago. H’ was signifi cantly lower in our area than in the previous study (t = 8.588, p <0.001), but equitability (J) was very similar. Several factors may contribute to these diff erences, including local diff erences in bee assemblage composition, diff erences in the probability of capturing the diff erent species (many rare species), factors affecting the sampling itself, and perhaps species loss over the three decades separating the two studies. The magnitude of species loss is difficult to assess because the two studies were not carried out exactly in the same area and there were differences in sampling time and sampling effort.

Comment on “Impacts of species richness on productivity in a large-scale subtropical forest experiment”

Science ◽  
2019 ◽  
Vol 363 (6423) ◽  
pp. eaav9117
Author(s):  
Hua Yang ◽  
Zhongling Guo ◽  
Xiuli Chu ◽  
Rongzhou Man ◽  
Jiaxin Chen ◽  
...  
Keyword(s):  
Species Richness ◽  
Tree Species ◽  
Large Scale ◽  
Forest Productivity ◽  
Subtropical Forest ◽  
Species Loss ◽  
Subtropical China

Huang et al. (Reports, 5 October 2018, p. 80) report significant increases in forest productivity from monocultures to multispecies mixtures in subtropical China. However, their estimated productivity decrease due to a 10% tree species loss seems high. We propose that including species richness distribution of the study forests would provide more meaningful estimates of forest-scale responses.

scholarly journals Decomposing phylogenetic entropy into α , β and γ components

2010 ◽  
Vol 7 (2) ◽  
pp. 205-209 ◽  
Author(s):  
Maud A. Mouchet ◽  
David Mouillot
Keyword(s):  
Species Richness ◽  
Phylogenetic Trees ◽  
Phylogenetic Diversity ◽  
Biological Diversity ◽  
Diversity Indices ◽  
Species Loss ◽  
Full Understanding ◽  
Abundance Distribution ◽  
Additive Decomposition ◽  
Weak Monotonicity

Measuring the phylogenetic diversity of communities has become a key issue for biogeography and conservation. However, most diversity indices that rely on interspecies phylogenetic distances may increase with species loss and thus violate the principle of weak monotonicity. Moreover, most published phylogenetic diversity indices ignore the abundance distribution along phylogenetic trees, even though lineage abundances are crucial components of biodiversity. The recently introduced concept of phylogenetic entropy overcomes these limitations, but has not been decomposed across scales, i.e. into α , β and γ components. A full understanding of mechanisms sustaining biological diversity within and between communities needs such decomposition. Here, we propose an additive decomposition framework for estimating α , β and γ components of phylogenetic entropy. Based on simulated trees, we demonstrate its robustness to phylogenetic tree shape and species richness. Our decomposition fulfils the requirements of both independence between components and weak monotonicity. Finally, our decomposition can also be adapted to the partitioning of functional diversity across different scales with the same desirable properties.

scholarly journals Weak conspecific feedbacks and exotic dominance in a species-rich savannah

2011 ◽  
Vol 278 (1720) ◽  
pp. 2939-2945 ◽  
Author(s):  
Andrew S. MacDougall ◽  
Matthias C. Rillig ◽  
John N. Klironomos
Keyword(s):  
Species Richness ◽  
Relative Strength ◽  
Feedback Stabilization ◽  
Species Loss ◽  
Plant Abundance ◽  
Field Surveys ◽  
Negative Feedbacks

Whether dominance drives species loss can depend on the power of conspecific self-limitation as dominant populations expand; these limitations can stabilize competitive imbalances that might otherwise cause displacement. We quantify the relative strength of conspecific and heterospecific soil feedbacks in an exotic-dominated savannah, using greenhouse trials and field surveys to test whether dominants are less self-suppressed, highly suppressive of others or both. Soil feedbacks can impact plant abundance, including invasion, but their implications for coexistence in invader-dominated systems are unclear. We found that conspecific feedbacks were significantly more negative than heterospecific ones for all species including the dominant invaders; even the rarest natives performed significantly better in the soils of other species. The strength of these negative feedbacks, however, was approximately 50 per cent stronger for natives and matched their field abundance—the most self-limited natives were rare and narrowly distributed. These results suggest that exotics dominate by interacting with natives carrying heavier conspecific feedback burdens, without cultivating either negative heterospecific effects that suppress natives or positive ones that accelerate their own expansion. These feedbacks, however, could contribute to coexistence because all species were self-limited in their own soils. Although the net impact of this feedback stabilization will probably interact with other factors (e.g. herbivory), soil feedbacks may thus contribute to invader dominance without necessarily being detrimental to species richness.

scholarly journals Impacts of species richness on productivity in a large-scale subtropical forest experiment

Science ◽  
2018 ◽  
Vol 362 (6410) ◽  
pp. 80-83 ◽  
Author(s):  
Yuanyuan Huang ◽  
Yuxin Chen ◽  
Nadia Castro-Izaguirre ◽  
Martin Baruffol ◽  
Matteo Brezzi ◽  
...  
Keyword(s):  
Species Richness ◽  
Primary Productivity ◽  
Ecosystem Functioning ◽  
Phylogenetic Diversity ◽  
Large Scale ◽  
Subtropical Forest ◽  
Species Loss ◽  
Shrub Species ◽  
Mitigate Climate Change ◽  
Functional And Phylogenetic Diversity

Biodiversity experiments have shown that species loss reduces ecosystem functioning in grassland. To test whether this result can be extrapolated to forests, the main contributors to terrestrial primary productivity, requires large-scale experiments. We manipulated tree species richness by planting more than 150,000 trees in plots with 1 to 16 species. Simulating multiple extinction scenarios, we found that richness strongly increased stand-level productivity. After 8 years, 16-species mixtures had accumulated over twice the amount of carbon found in average monocultures and similar amounts as those of two commercial monocultures. Species richness effects were strongly associated with functional and phylogenetic diversity. A shrub addition treatment reduced tree productivity, but this reduction was smaller at high shrub species richness. Our results encourage multispecies afforestation strategies to restore biodiversity and mitigate climate change.

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