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opencc-by-4.0Feb 2021View details →

paperChain - Video Animation - Circular Case 3 (Slovenia)

This animation video summarises in approximately two minutes the most relevant results of the implementation of paperChain's Circular Case.

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paperChain - Video Animation - Circular Case 1 (Portugal)

This animation video summarises in approximately two minutes the most relevant results of the implementation of paperChain's Circular Case.

opencc-by-4.0Jun 2021View details →

paperChain - Video Animation - Circular Case 1 (Portugal) - Portuguese version

This animation video summarises in approximately two minutes the most relevant results of the implementation of paperChain's Circular Case.

Fig. 4 in Animal use of rehabilitated formerly fire damaged peat-swamp forest in western Sabah, Malaysia

Fig. 4. Temporal activity patters for the nine most frequently photographed animal species in the northern part of Klias Forest Reserve, Sabah, Malaysia. Rehabilitated forest (L); Intact forest (R). Black bars indicate nocturnal activity; dotted bars indicate diurnal activity. Number in parenthesis represents number of independent camera trap records.

Fig. 3 in Animal use of rehabilitated formerly fire damaged peat-swamp forest in western Sabah, Malaysia

Fig. 3. The observed species accumulation curves in rehabilitated forest (solid lines) versus intact forest (dashed lines) and their 95% Confidence Intervals for all animals detected (L) and for mammal species only (R) in Klias Forest Reserve. The curves were constructed using an abundance-based rarefaction approach with 100 randomisation runs in EstimateS (Colwell, 2013).

Fig. 1 in Animal use of rehabilitated formerly fire damaged peat-swamp forest in western Sabah, Malaysia

Fig. 1. Klias Forest Reserve and Binsulok Forest Reserve located in the Klias Peninsula in south-western Sabah, northern part of Malaysian Borneo (inset).

Fig. 2 in Animal use of rehabilitated formerly fire damaged peat-swamp forest in western Sabah, Malaysia

Fig. 2. Maps of the Normalised Difference Vegetation Index (NDVI) of the northern part of Klias Forest Reserve indicating the burnt forest areas (white) in 1998 (L) and the same study area in 2016 including oil palm plantations (white) in the north and eastern part of the reserve (R). Red circles indicate locations of camera trapping points in rehabilitated/burnt areas; Yellow circles indicate locations of camera trapping points in intact/unburnt areas.

opencc-by-4.0Feb 2013View details →

Fig.1. Bipartite graph depicting a plant-animal mutualistic network involving 10 in The Role Of Macaca Spp. (Primates: Cercopithecidae) In Seed Dispersal Networks

Fig.1. Bipartite graph depicting a plant-animal mutualistic network involving 10 frugivores (left) and 170 of the plant species (right) they disperse at Khao Yai National Park, Thailand. The list of plant species is based on Kitamura et al. (2002), then the list of frugivores dispersing each species has been completed thanks to data from bin Kassim (1987), Kitamura et al. (2005), Datta & Rawat (2008), Brockelman (2009), McConkey & Brockelman (2011), Albert et al. (2013), Ngoprasert (2012), Khamcha (pers. comm.), Latinne (pers. comm.), Martmoon (pers. comm.).

opencc-by-4.0Sep 2018View details →

Fig. 3 in Camera trapping of terrestrial animals in Tanjung Datu National Park, Sarawak, Borneo

Fig. 3. Activity pattern for selected species in Tanjung Datu National Park showing Dhat1 as an estimator of overlap (shaded area). Dhat1 compares curves at n.grid (number of points to estimate density for species comparison) and best for small samples. Dhat1 coefficient estimator ranges from 0–1.

opencc-by-4.0Sep 2018View details →

Fig. 2 in Camera trapping of terrestrial animals in Tanjung Datu National Park, Sarawak, Borneo

Fig. 2. Species accumulation curve in Tanjung Datu National Park indicates that the sampling saturation is almost reaching an asymptote.

opencc-by-4.0Sep 2018View details →

Fig. 1 in Camera trapping of terrestrial animals in Tanjung Datu National Park, Sarawak, Borneo

Fig. 1. Tanjung Datu National Park located at the tip of Borneo bordering Kalimantan, Indonesia with camera trap sites. Map of Sarawak indicating locations of Sarawak's protected areas. Tanjung Datu National Park map adapted from Hazebroek & Abang (2000).

Figure 5 in Long-bone geometry in columnar-limbed animals: allometry of the proboscidean appendicular skeleton

Figure 5. Independent contrasts reduced major axis (RMA) regression plots for the total sample of proboscideans. Slopes and correlations, respectively, are 1.079 and 0.902 (humerus), 0.961 and 0.841 (ulna), 0.761 and 0.857 (femur), and 0.828 and 0.873 (tibia).

Figure 3 in Long-bone geometry in columnar-limbed animals: allometry of the proboscidean appendicular skeleton

Figure 3. Morphometric comparisons of humereral and femoral proportions., Loxodonta africana; A, Elephas maximus, Z, Mammuthus (columbi, imperator, meridionalis, and primigenius); Δ, gomphotheres s.l. (Archaeobelodon filholi, Cuvieronius hyodon, Eubelodon morrilli, Gomphotherium angustidens, Gomphotherium productum, Mammut americanum, Serbelodon barbourensis, and Stegomastodon platensis).

Figure 2 in Long-bone geometry in columnar-limbed animals: allometry of the proboscidean appendicular skeleton

Figure 2. Phylogenetic tree structure of the 19 included proboscidean genera, along with inferred clade ages. References used in constructing the tree topology and assigning clade ages were Tassy & Pickford (1983), Tassy (1994, 1995a, b, c), Lister (1995), Kalb et al. (1995), Lambert (1995), Saunders (1995), Shoshani (1995b), Shoshani & Tassy (1995b), Shoshani et al. (1995, 1998), Tobien (1995), Todd & Roth (1995), Gheerbrant et al. (1996), and Thomas et al. (2000).

Figure 1 in Long-bone geometry in columnar-limbed animals: allometry of the proboscidean appendicular skeleton

Figure 1. Proboscidean limb bones: 1–5, humeri; 6–10, femora. 1 and 6, Loxodonta africana; 2 and 7, Elephas maximus; 3 and 8, Mammuthus imperator; 4 and 9, Stegomastodon superbus; 5 and 10, Mammut americanum.

Figure 11 in Hybridization in the evolution of animal form and life-cycle

Figure 11. Four mid-Cambrian species from the Burgess Shale of British Columbia. A, Laggania cambria (= Anomalocaris nathorsti), ventral; B, Anomalocaris canadensis, ventral; C, Amiskwia sagittiformis; D, Nectocaris pteryx. Scale bar = ∼200 mm (A, B), ∼5 mm (C, D). [A, B reproduced with permission from S M Gonn III (from 'The Anomalocarid Bauplan' http://www.geocities.com/goniagnostus/background3.html); C, D, from Marianne Collins in Gould, 1989.]

Figure 9 in Hybridization in the evolution of animal form and life-cycle

Figure 9. Reticulate phylogeny of adults and larvae of extant hemichordates and echinoderms, showing probable sequence of events. Time (horizontal) not to scale. Ord/Sil, Ordovician/Silurian boundary; pres, present; thick black lines, adults; thin black lines, larvae; grey arrows, larval transfers.

Figure 7. Two Cambrian trilobites. A–D in Hybridization in the evolution of animal form and life-cycle

Figure 7. Two Cambrian trilobites. A–D, stages in the development of Sao hirsute: A, protaspis; B–D, early segmented stages. E, adult Agnostus pisiformis. Scale bar = ∼1 mm (A–D from Borradaile et al., 1935; E redrawn after Fortey, 2000.)

Figure 6 in Hybridization in the evolution of animal form and life-cycle

Figure 6. Stages in the development of the branchiopod crustacean Leptestheria syriaca, to different magnifications. (From Gurney, 1942; as Estheria.)

Figure 5. A in Hybridization in the evolution of animal form and life-cycle

Figure 5. A, nauplius of Penaeus sp. (recent Crustacea: Penaeidae). B, C, Martinssonia elongata (upper Cambrian): B, paranauplius II (left first appendage omitted); C, oldest known stage. Scale bar = ∼0.1 mm (A after Gurney, 1942; B, C adapted from Müller & Walossek, 1986b.)