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FIGURE 2 in Genetic diversity and aquaculture conservation for a threatened Neotropical catfish

FIGURE 2 | Attributions of Lophiosilurus alexandri genotypes from A. captive broodstocks (Bebedouro, Paulo Afonso, and Itiúba) and wild samples taken from two stretches of the São Francisco River (upper and submiddle) and B. only for the wild samples. Each vertical bar represents a different individual and the length is proportional to the inferred group, cluster 1 (red) and cluster 2 (green). Respective estimated K value through log-likelihood. Y axis for delta (K) values and X axis for different K values tested.

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FIGURE 1 in Genetic diversity and aquaculture conservation for a threatened Neotropical catfish

FIGURE 1 | Map showing the São Francisco River Basin with locations of the three restocking hatcheries () of Lophiosilurus alexandri and an experimental laboratory (LAQUA). The wild samples taken in the upper and submiddle stretches are denoted by.

opencc-by-4.0Dec 2020View details →

FIGURE 2 in A Century after! Rediscovery of the ancient catfish Diplomystes Bleeker 1858 (Siluriformes: Diplomystidae) in coastal river basins of Chile and its implications for conservation

FIGURE 2 | Individuals of Diplomystes nahuelbutaensis recorded in this study and their habitat. A. individual collected in Laraquete (Lar01); B. individual collected and released in Carampangue. C. individual collected in Laraquete (Lar02) and released; D. Habitat of D. nahuelbutaensis in the Cabrera River, Carampangue Basin.

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FIGURE 4 in A Century after! Rediscovery of the ancient catfish Diplomystes Bleeker 1858 (Siluriformes: Diplomystidae) in coastal river basins of Chile and its implications for conservation

FIGURE 4 | Null distribution of Fst values assuming a panmictic model versus the observed Fst value (vertical line) between Coastal and Biobío samples of Diplomystes nahuelbutaensis.

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Figure 1. A in Habitat description of the rare orchid Didymoplexis verrucosa for more effective conservation

Figure 1. A, Location of the province of KwaZulu-Natal within South Africa; B, northern KwaZulu-Natal showing the very limited extent of remaining forest ecosystems shaded in black with degree grid lines for spatial reference; C, study area shaded in grey south of the coastal town of Mtunzini with quarter degree grid lines for spatial reference.

Figure 4 in Dung beetle conservation in a heterogeneous landscape of the Maputaland Centre of Endemism

Figure 4. Contribution of each spatial component (habitat and patch size) to total species numbers sampled in the entire reserve (gamma diversity, n = 61 species); alpha (α) = diversity contributed by study sites; beta (β1) = diversity between study sites; beta (β2) = diversity between habitats. Proportions contributed by alpha and beta diversity are shown by the divisions within the bars whereas numbers of species are shown inside the bars (see methods). DF = dune forest; SF-L, SF-M, SF-S = large, medium and small sand forest patches; G = grassland.

Figure S1 in Dung beetle conservation in a heterogeneous landscape of the Maputaland Centre of Endemism

Figure S1. Rarity index values for each species ranked from highest to lowest. Dotted lines show rare species found at up to two sites and indicate the high proportion of the total species (~60%) found at eight sites or less (key to blocks of species numbers in Table S1; species in bold biased to grassland occurrence).

Figure 3 in Dung beetle conservation in a heterogeneous landscape of the Maputaland Centre of Endemism

Figure 3. Box plots comparing number of species (A) and abundance (B) in each habitat type (DF = dune forest, SF-L, SF-M, SF-S = large, medium and small sand forest patches, G = grassland). Within each box, the mid-line represents the median whereas the lower and upper extents of the box represent the interquartile range Q1 = 25th percentile and Q3 = 75th percentile, respectively. Whiskers are minimum and maximum values. Black points represent outliers. Different letters indicate statistical differences at P <0.05.

Figure 2 in Dung beetle conservation in a heterogeneous landscape of the Maputaland Centre of Endemism

Figure 2. Frequency distribution for proportions of species recorded at 32 study sites in MSR (n = 4 in dune forest; n = 7 in grassland and each of three patch sizes of sand forest). Dotted lines delineate the relative incidence of rar- er species at study sites. Note that a high percentage of the total species are found only in 25% of the sampled sites. See Figure S1 for values of the species rarity index.

Figure 1. A in Dung beetle conservation in a heterogeneous landscape of the Maputaland Centre of Endemism

Figure 1. A, map outlining the study area and showing the position of Maputo Special Reserve (MSR) in relation to land usage in the surrounding area of southeast Mozambique and northeast KwaZulu-Natal, South Africa (nature and game reserves are marked by green and yellow, darker grey outlines the Lubombo Conservancy, unprotected areas are pale grey, Indian Ocean, inlets and lagoons are blue) (redrawn from Peace Parks Foundation 2020); B, position of sampling localities in MSR plotted onto Google Earth; L1–L7 = study sites at each locality in large, medium and small sand forest patches plus grassland; L8, DF1–DF4 = dune forest study sites. Position of most forest sites was measured at the point of entry as the GPS could not detect satellites under the canopy.

Fig. 4 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 4 - Qualitative-quantitative distribution of wintering Kentish plovers along the Sicilian coast. The maximum concentration of birds in a single observation was recorded in the area of "Capo Feto", with a flock of 70 ind. / Distribuzione quali-quantitativa degli individui svernanti di fratino lungo la costa siciliana. La massima concentrazione in una singola osservazione è stata registrata nella zona di "Capo Feto", con un gruppo di 70 ind.

Fig. 2 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 2 - Past and present distribution of the Kentish Plover in Sicily. / Distribuzione passata e presente del fratino in Sicilia. Recorded in earlier atlases (Massa, 1985; Lo Valvo et al., 1993), but not confirmed during the present study. / Rilevato in atlanti precedenti (Massa, 1985; Lo Valvo et al., 1993), ma non confermato da questo studio. ∆ Unpublished records not reported in earlier atlases (Massa, 1985; Lo Valvo et al., 1993; AA.VV., 2008) and not confirmed during the present study. / Dati non pubblicati nei precedenti atlanti (Massa, 1985; Lo Valvo et al., 1993; AA.VV., 2008) e non confermati da questo studio. Presence recorded in AA.VV. (2008), but not confirmed during the present study. / Presenza rilevata in AA.VV. (2008), ma non confermata da questo studio. ● Presence recorded in AA.VV. (2008) and confirmed during the present study / Rilevato in AA.VV. (2008) e confermato in questo studio. ■ New record in comparison to the last atlas (2008). / Nuova presenza rispetto all'ultimo atlante (2008).

Fig. 1 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 1 - Kentish plover female with chicks at "Triscina" beach (Trapani), June 2019. / Femmina di fratino con pulcini sulla spiaggia di "Triscina" (TR), Giugno 2019 (Photo/Foto: A. Barbera).

Fig. 12 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 12 - Roccazzelle beach, Gela: sandy coast with "Torre Manfria" on the background. / Spiaggia di Roccazzelle, Gela: costa sabbiosa con "Torre Manfria" sullo sfondo (Photo / Foto: M. Zafarana).

Fig. 5 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 5 - Typical breeding habitat of the Kentish plover in "Saline di Trapani". / Tipico habitat riproduttivo del fratino nel sito "Saline di Trapani". (Photo / Foto: G. Spinella).

Fig. 3 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 3 - Qualitative-quantitative distribution of Kentish plover breeding pairs along the Sicilian coast. Maximum concentrations of pairs were in the areas of "Saline di Trapani e Marsala", "Capo Feto" and along the sandy coast of the Gulf of Gela. / Distribuzione quali-quantitativa delle coppie nidificanti di fratino lungo la costa siciliana. Le massime concentrazioni di coppie si sono registrate nelle aree di "Saline di Trapani e Marsala", "Capo Feto" e lungo la costa sabbiosa del Golfo di Gela.

Fig. 6 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 6 - The beach of "Capo Feto", one of the most important breeding and wintering sites for the Kentish plover in Sicily. / La spiaggia di "Capo Feto", uno dei più importanti siti di riproduzione e svernamento del fratino in Sicilia (Photo / Foto: A. Barbera).

Fig. 13 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 13 - The coastline of Siculiana Marina, Agrigento. / La costa di Siculiana Marina, Agrigento. (Photo / Foto: R. Ientile).

Fig. 14 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 14 - Preference of nesting habitat in the 8 Sicilian provinces based on 193 confirmed nests records. / Ambienti di nidificazione preferenziali nelle 8 province siciliane sulla base di 193 record di nidificazione confermati.

Fig. 10 in Status, distribution and conservation of Kentish plover Charadrius alexandrinus (Aves, Charadriiformes) in Sicily

Fig. 10 - Massolivieri, Syracuse: the rocky coast of Penisola Maddalena, a breeding and wintering site used by the Kentish plover. / Massolivieri, Siracusa: la costa rocciosa di Penisola Maddalena, sito di riproduzione e svernamento utilizzato dal fratino (Photo / Foto: R. Ientile).