Anat Feldman’s research while affiliated with Tel Aviv University and other places

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Publications (4)


Reptile responses to anthropogenic habitat modification: A global meta-analysis
  • Article

March 2020

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710 Reads

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125 Citations

Global Ecology and Biogeography

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Aim The aim was to determine how reptile populations respond to anthropogenic habitat modification and determine whether species traits and environmental factors influence such responses. Location Global. Time period 1981–2018. Major taxa studied Squamata. Methods We compiled a database of 56 studies reporting how habitat modification affects reptile abundance and calculated standardized mean differences in abundance (Hedges’ g ). We used Bayesian meta‐analytical models to test whether responses to habitat modification depended on body size, clutch size, reproductive mode, habitat specialization, range size, disturbance type, vegetation type, temperature and precipitation. Results Based on 815 effect sizes from 376 species, we found an overall negative effect of habitat modification on reptile abundance (mean Hedges’ g = −0.43, 95% credible intervals = −0.61 to −0.26). Reptile abundance was, on average, one‐third lower in modified compared with unmodified habitats. Small range sizes and small clutch sizes were associated with more negative responses to habitat modification, although the responses were weak and the credible intervals overlapped zero. We detected no effects of body size, habitat specialization, reproductive mode (egg‐laying or live‐bearing), temperature or precipitation. Some families exhibited more negative responses than others, although overall there was no phylogenetic signal in the data. Mining had the most negative impacts on reptile abundance, followed by agriculture, grazing, plantations and patch size reduction, whereas the mean effect of logging was neutral. Main conclusions Habitat modification is a key cause of reptile population declines, although there is variability in responses both within and between species, families and vegetation types. The effect of disturbance type appeared to be related to the intensity of habitat modification. Ongoing development of environmentally sustainable practices that ameliorate anthropogenic impacts is urgently needed to prevent declines in reptile populations.


Histograms for oviparous (light grey), and viviparous (dark grey), squamate species. (a) Offspring masses (log 10 transformed, in g. (b) Brood sizes (mean number of eggs or neonates per clutch or litter, after logarithmic transformation). (c) Reproductive Investment (RI total mass of offspring in a clutch divided by the mass of the mother)
Egg mass at laying (x‐axis, in grams) relative to offspring mass at hatching (y‐axis, in grams) in squamate species laying variable clutch sizes. Both variables are log10‐transformed. R² = .96
Viviparity does not affect the numbers and sizes of reptile offspring
  • Article
  • Full-text available

December 2019

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163 Reads

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27 Citations

Viviparity (live‐bearing) has independently evolved from oviparity (egg‐laying) in more than 100 lineages of squamates (lizards and snakes). We might expect consequent shifts in selective forces to affect per‐brood reproductive investment (RI = total mass of offspring relative to maternal mass) and in the way in which that output is partitioned (number vs. size of offspring per brood). Based on the assumption that newly born offspring are heavier than eggs, we predicted that live‐bearing must entail either increased RI or a reduction in offspring size and/or fecundity. However, our phylogenetically controlled analysis of data on 1,259 squamate species revealed no significant differences in mean offspring size, clutch size or RI between oviparous and viviparous squamates. We attribute this paradoxical result to (1) strong selection on offspring sizes, unaffected by parity mode, (2) the lack of a larval stage in amniotes, favouring large eggs even in the ancestral oviparous mode and (3) the ability of viviparous females to decrease the mass of uterine embryos by reducing extra‐embryonic water stores. Our analysis shows that squamate eggs (when laid) weigh about the same as the hatchlings that emerge from them (despite a many‐fold increase in embryo mass during incubation). Most of the egg mass is due to components (such as water stores and the eggshell) not required for oviductal incubation. That repackaging enables live‐born offspring to be accommodated within the mother's body without increasing total litter mass. The consequent stasis in reproductive burden during the evolutionary transition from oviparity to viviparity may have facilitated frequent shifts in parity modes.

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Fig. 1 | Species richness maps of terrestrial tetrapods. a, Richness of all tetrapods (reptiles, amphibians, birds and mammals). b-e, Species richness of reptile groups: all reptiles (b), lizards (c), snakes (d) and turtles (e). Grey areas denote terrestrial regions devoid of species in a particular group. Blue colours denote regions with few species and red ones denote regions with many species (note that the scale differs between panels). All maps in an equal area, Behrmann projection at a 48.25 × 48.25 km grid-cell resolution), scale bar values represent species richness. 
Fig. 2 | Comparing reptile richness to other tetrapods. a-c, Hexagon scatter plots comparing species richness values per grid-cell with binning (black line indicates a LOESS fit, α = 0.6) of tetrapods without reptiles to all reptiles (a), lizards (b) and snakes (c). d, Map of the ratio of reptile richness to nonreptilian tetrapod richness per grid-cell (note the wide range of values for the top category). Hatched regions designate areas where this proportion is the top 5% (black) and 25% (grey). 
Fig. 3 | Species richness hotspots of reptiles and reptile groups. a-d, In each panel the lightest colour denotes the 10% of 48.25 × 48.25 km gridcells with the highest numbers of species, and as the colours get darker they represent the top 7.5%, 5% and richest 2.5% cells. Panels show all reptiles (a), lizards (b), snakes (c) and turtles (d).
Fig. 4 | Key areas for tetrapod conservation, highlighting regions that rise in importance for conservation due to inclusion of reptiles. Cells were ranked in a formal prioritization scheme 20 , based on complementarity when ranking cells in an iterative manner. Cells were ranked twice: (1) with all tetrapods and (2) with all tetrapods excluding reptiles. a, Patterns per 0.5 degree grid-cell where colours represent the priority ranks for the scheme that included all tetrapods (blue = low, red = high). The cells that are highlighted with the bold foreground colours are those that pinpoint those regions that gain in conservation importance due to the inclusion of the reptile data. These cells were selected following two rules: (1) they were in the top 10% of increase in rank, when subtracting the ranks of the analysis with reptiles from the ranks of the analysis without them; and (2) were part of statistically significant spatial clusters of rank changes (using local Moran's I 35 ). b, The mean change in rank between prioritizations with and without reptiles (using the above method) per ecoregion (red, ecoregions that become more important due to the inclusion of reptile information; blue, ecoregions becoming less important). 
Publisher Correction: The global distribution of tetrapods reveals a need for targeted reptile conservation

November 2017

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1,472 Reads

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7 Citations

Nature Ecology & Evolution

In this Article originally published, owing to a technical error, the author ‘Laurent Chirio’ was mistakenly designated as a corresponding author in the HTML version, the PDF was correct. This error has now been corrected in the HTML version. Further, in Supplementary Table 3, the authors misspelt the surname of ‘Danny Meirte’; this file has now been replaced.

Citations (4)


... Reptiles are among the most threatened groups of vertebrates globally, with habitat loss and fragmentation being major drivers of their current decline [24]. Agricultural intensification, which often involves the removal of natural vegetation, the use of pesticides added to the indirect loss of prey, and the simplification of landscape structure, has been shown to negatively impact biodiversity as a whole [25] and reptiles in particular [26]. However, low-intensity farming systems, which mimic natural habitats and maintain structural complexity, can provide suitable conditions for reptiles, indicating that semi-natural patches of traditional cultural landscape can support diverse reptile communities, particularly when they are embedded in a heterogeneous landscape with patches of natural vegetation (e.g., [11]). ...

Reference:

Ecological Connectivity for Reptiles in Agroecosystems: A Case Study with Olive Groves in Liguria (Northwestern Italy)
Reptile responses to anthropogenic habitat modification: A global meta-analysis
  • Citing Article
  • March 2020

Global Ecology and Biogeography

... Determining the costs and adaptive benefits of viviparity is fundamental to understanding why viviparity evolves. Relative to oviparity, viviparity appears to impose more restrictions on female reproductive output and incurs a greater cost per reproductive event (48)(49)(50). Yet viviparity must increase relative fitness in some situations because it has evolved multiple times and persisted over millions of years of evolutionary history (46). ...

Viviparity does not affect the numbers and sizes of reptile offspring

... UGI is important for the provision of ecosystem services, including pollination, in urban areas (Niemel€ a et al., 2010). However, from the perspective of the conservation of biodiversity, the potential of UGI is unclear, as there is considerable variation in the capacity of different taxa to persist in urbanized regions (McDonnell & Hahs, 2015;Venn, Novitsky, Vershinin, & Kreuzberg, 2018). Urban and peri-urban areas (Snep et al., 2006) contain many habitats with resources for pollinating insects. ...

Status, trends and future dynamics of biodiversity and ecosystems underpinning nature's contributions to people

... The habitat of amphibians and reptiles in the area are in an extensive transition23. Research shows that isolation is the primary cause of the differentiation of reptilian fauna, and the four chorotypes from the geographical fauna analysis of reptiles in eastern China did not refer to the Tibetan Plateau and the arid land of northwest China24,25.The distribution of amphibians, birds and mammals have underpinned global and local conservation pri- orities and are fundamental to the understanding of the determinants of global biodiversity26. One of the most important objectives in ecology is to understand why species exist in one place and not in another. Distributional models are based on (usually) limited records of presence and absence, predicting where species will occur, given a correlation with one or more ecological variables27. ...

Publisher Correction: The global distribution of tetrapods reveals a need for targeted reptile conservation

Nature Ecology & Evolution