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Figure 6 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Figure 6 Scincid, gerrhosaurid and oplurid species identified in this study. Sampling localities for each photographed individual are provided. ANP ES – Andringitra National Park Eastern Slopes; ANP WS – Andringitra National Park Western Slopes (Fig. 1; Suppl. material 1: Table S1). A.Oplurus grandidieri from Anja; B.Oplurus quadrimaculatus from Anja; C.Zonosaurus laticaudatus from Anja; D.Zonosaurus ornatus from Antanifotsy 2; E.Zonosaurus aeneus from Namoly; F.Trachylepis elegans from Iantaranomby (ANP WS); G.Trachylepis gravenhorstii from Anja; H.Trachylepis sp. aff. vato from Asaramanitra (ANP ES); I.Trachylepis boettgeri from Antanifotsy 3. Photographs by Javier Lobón-Rovira.
Figure 1 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Figure 1 Map of the study area and sampling sites. The borders of Andringitra National Park (red) and Paysage Harmonieux Protégé du Corridor Forestier Ambositra–Vondrozo (Ambositra–Vondrozo Forest Corridor) (blue) are shown. See Suppl. material 1: Table S1 for more details on the sampled localities. Map data ©2015 Google (QGIS Development Team 2020). ANP ES – Andringitra National Park Eastern Slopes; ANP WS – Andringitra National Park Western Slopes. A. Anja; B. Sakaviro; C. Ambatomainty; D. Western slopes of the Andringitra Massif from Iantaranomby (ANP WS); E. Imaitso (ANP ES); F. Belambo (ANP ES); G. Fivahona–Velotsoa; H. Map with sampling sites. Photographs by Javier Lobón-Rovira.
Figure 4 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Figure 4 Chameleonid species identified in this study. The picture of the individual identified as Furcifer willsii from Fivahona–Velotsoa, found within the stomach content of a Mimophis mahfalensis, is not shown. Sampling localities for each photographed individual are provided. ANP ES – Andringitra National Park Eastern Slopes; ANP WS – Andringitra National Park Western Slopes (Fig. 1; Suppl. material 1: Table S1). A.Brookesia brunoi from Anja; B.Calumma andringitraense from Imaitso (ANP ES); C.Calumma crypticum from Imaitso (ANP ES); D.Calumma fallax from Asaramanitra (ANP ES); E.Palleon nasus from Namoly; F.Furcifer lateralis from Iantaranomby (ANP WS); G.Furcifer major from Anja; H.Furcifer nicosiai from Tsaranoro; I.Furcifer oustaleti from Anja. Photographs by Javier Lobón-Rovira.
Supplementary material 3 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Table S3. Amphibian samples identified in this study
Supplementary material 8 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Reptiles Neighbor joining tree of the cytochrome oxidase I gene
Supplementary material 4 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Table S4. Reptile samples identified in this study
Supplementary material 2 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Table S2. Amplified genes, primers and PCR conditions used in this study
Supplementary material 7 from: Belluardo F, Quirós DD, Lobón-Rovira J, Rosa GM, Rasoazanany M, Andreone F, Crottini A (2021) Uncovering the herpetological diversity of small forest fragments in south-eastern Madagascar (Haute Matsiatra). Zoosystematics and Evolution 97(2): 315-343. https://doi.org/10.3897/zse.97.63936
Figure S1. Amphibians Neighbor joining tree of the 16S rRNA gene 3' terminus
Figure 2 in Nest-site microhabitat association of red-billed leiothrix in subtropical fragmented forest in central China: evidence for a reverse edge effect on nest predation risk?
Figure 2. Nest sites of red-billed leiothrix (a) in the forest and (b) in the scrub-grassland.
Figure 5 in The social wasps (Hymenoptera: Vespidae: Polistinae) of a fragment of Atlantic Forest in southern Bahia, Brazil
Figure 5. Number of wasps collected at different times of the day in the three fragments.
Figure 1 in The social wasps (Hymenoptera: Vespidae: Polistinae) of a fragment of Atlantic Forest in southern Bahia, Brazil
Figure 1. Location of the Michelin Ecological Reserve (MER).
Figure 3 in The social wasps (Hymenoptera: Vespidae: Polistinae) of a fragment of Atlantic Forest in southern Bahia, Brazil
Figure 3. Dendrogram of similarity among wasp surveys carried out in the Atlantic Forest.
Figure 2 in The social wasps (Hymenoptera: Vespidae: Polistinae) of a fragment of Atlantic Forest in southern Bahia, Brazil
Figure 2. Location of the transects carried out in the Atlantic Forest.
Habitat fragmentation and logging affects the occurrence of the lesser mouse deer in tropical forest reserves
<p>Due to rapid urbanization, logging, and agricultural expansion, forest fragmentation is negatively affecting native wildlife populations throughout the tropics. <span>This study examined the effects of landscape and habitat characteristics on the lesser </span>mouse deer, <i>Tragulus kanchil,</i><span> populations in Peninsular Malaysia. A total of 315 camera traps were deployed in eight forest reserves. This study provides critical ecological information for managing and conserving understudied populations of <i>T. kanchil</i>. We found that the detection of <i>T. kanchil </i>was attributed to forest fragmentation.<i> </i>Forest patches had the detection of <i>T. kanchil</i> four times greater than continuous forests<i>. </i>The detection of <i>T. kanchil</i> was nearly three times higher in the peat swamp forest compared to the lowland dipterocarp forests. Surprisingly, the detection of <i>T. kanchil</i> was almost twice lower in the unlogged forests compared to logged forests. The detection of <i>T. kanchil</i> increased with the presence of trees, particularly those with DBH of 5 cm to 45 cm, canopy cover, number of saplings</span> <span>and palms, number of dead fallen trees, and distance from nearest roads. However, detection decreased with a greater number of trees with a DBH greater than 45 cm and higher elevation. We recommend that conservation stakeholders take the necessary steps to support the conservation of mouse deer species and its natural habitats regardless of whether these forests are fragmented or continuous. These steps include eradicating poaching, habitat degradation, and further deforestation.</span></p>
Figure 3 from: Tajovsky K, Hosek J, Hofmeister J, Wytwer J (2012) Assemblages of terrestrial isopods (Isopoda, Oniscidea) in a fragmented forest landscape in Central Europe. ZooKeys 176: 189-198. https://doi.org/10.3897/zookeys.176.2296
Figure 3 - A triplot of the RDA block analyses of terrestrial isopod assemblages at the sites studied. For the abbreviations of the species see Table 1, FA – fragment area, C/N – carbon-nitrogen ratio, Ca2+ – calcium content of the soil, pHH2O – soil acidity. TO, MOH, TOH, AO, BO, BOH, MDF, DP and CP – vegetation at the different sites, see text.
Figure 2 from: Tajovsky K, Hosek J, Hofmeister J, Wytwer J (2012) Assemblages of terrestrial isopods (Isopoda, Oniscidea) in a fragmented forest landscape in Central Europe. ZooKeys 176: 189-198. https://doi.org/10.3897/zookeys.176.2296
Figure 2 - Epigeic activity (columns) (total catch per 5 traps per year) and numbers of species (white squares) of isopods at the sites studied in the different fragments of woodland.
Figure 1 from: Tajovsky K, Hosek J, Hofmeister J, Wytwer J (2012) Assemblages of terrestrial isopods (Isopoda, Oniscidea) in a fragmented forest landscape in Central Europe. ZooKeys 176: 189-198. https://doi.org/10.3897/zookeys.176.2296
Figure 1 - Total population densities (ind.m-2 ± SE) (columns) and numbers of species (white squares) in the isopod assemblages at the sites sampled in the different fragments of woodland.
FIG. 4 in Multi-aged forest fragments in Atlantic France that are surrounded by meadows retain a richer epiphyte lichen flora
FIG. 4. — The significant effect of canopy density on lichen abundance according to the summary of the GLMMs. The GLMM results are presented for the exterior forest at the tree level within the FFs surrounded by meadows, taking into account the larger tree category (details as in Fig. 2).
FIG. 3 in Detangling the effects of patch attributes on bryophyte diversity in fragmented subtropical secondary forests - a case study of land-bridge islands
FIG. 3. — Relationships of species richness with number of habitat type, area, elevation, shape irregularity, vegetative cover, and ISW for 13 bryophyte families in 168 forest fragments of the Thousand Island Lake, China. The regression equations are derived from GLMMs. Note: ISW, the relative proportion of water within a circle of a diameter of 1000 m centered on a given island.
Code for 'Pronounced impacts of fragmentation on global forest resilience'
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