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37 results for “Central Sands”
Figure 8 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 8 Advertisement call of Adenomera albarena (A, B) and A. simonstuarti sensu stricto (C, D). A, B.INPA-H 44876 (FNJV 59564), Rio Negro Sustainable Development Reserve, Iranduba, Amazonas, Brazil. C, D.INPA-H 44904 (FNJV 59568), Tarauacá, Acre, Brazil.
Figure 7 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 7 Dorsal, ventral and lateral views of the three colour patterns of Adenomera albarena in preservative. Paratypes: A–C. (INPA-H 44869, male); D–F. (INPA-H 44870, male) and G–I (INPA-H 44877, male). Photographs: L. R. Mendonça. Scale bar: 5 mm.
Figure 4 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 4 Male holotype and female paratype of Adenomera albarena. A–C. Male holotype, INPA-H 44867; D–F. Female paratype INPA-H 44875. Scale bar: 5 mm.
Figure 3 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 3 Morphometric Principal Component Analysis. Analyses were based on 15 morphometric ratios of 21 males of Adenomera sp. nov. and 14 males of A. simonstuarti sensu stricto. Ellipse represents the standard error with 95% confidence interval.
Figure 2 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 2 Phylogenetic relationships of the Adenomera andreae species clade with a focus on the A. simonstuarti species complex. Maximum Likelihood values are inferred from sequence data for Cytb, COI, RAG1 and POMC genes. Lineage numbering within A. simonstuarti species complex follows Carvalho et al. (2020b), except for A. simonstuarti sensu stricto (SS). Species names are followed by the corresponding museum voucher numbers. Symbols are as in Fig. 1.
Figure A1 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure A1 Adenomera simonstuarti from the Municipality of Tarauacá, State of Acre, Brazil. Dorsal and ventral views of males (A–D) and females (E–F). A, B.INPA-H 44905, SVL 25.2 mm; C, DINPA-H 44912, SVL 24.5 mm; E, F.INPA-H 44909, SVL 23.0 mm. Photographs: L. R. Mendonça.
Figure 10 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 10 Natural history of Adenomera albarena. A. Example of the species' habitat; B. Unvouchered male vocalising on leaf litter; C. Unvouchered female hiding in the leaf litter; D. Foam nest, artificially exposed for illustration purpose. Scale bar: ~ 5 mm.
Figure 1 from: Martins BdaC, Tamanini Mônico A, Mendonça C, Dantas SP, Souza JRD, Hanken J, Lima AP, Ferrão M (2024) A new species of terrestrial foam-nesting frog of the Adenomera simonstuarti complex (Anura, Leptodactylidae) from white-sand forests of central Amazonia, Brazil. Zoosystematics and Evolution 100(1): 233-253. https://doi.org/10.3897/zse.100.110133
Figure 1 Geographic distribution of the Adenomera simonstuarti species complex (left) and a detailed view of the geographic distribution of the new species in central Amazonia, Amazonas, Brazil (right). Green area: Rio Negro Sustainable Development Reserve. Numbers: permanent sampling modules at (1) km 18, (2) km 26 and (3) km 50 along the AM-352 highway; (4) Vale da Benção Community, Ramal do 25, Manacapuru. South American countries: ARG, Argentina; BOL, Bolivia; CHL, Chile; COL, Colombia; ECU, Ecuador; PAR, Paraguay; PER, Peru; VEN, Venezuela.
FIGURE 5 in Taxonomy of the Sand Sliders of Western Australia's central coast (genus Lerista, Squamata: Scincidae): recognition of Lerista miopus (Günther, 1867)
FIGURE 5. Purported type of Soridia miopus Günther, 1867, BMNH1946.8.15.60. Photo by H.G. Cogger.
Fig 4 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 4 Mean values (min-max and ±SE) of species number and frequency of habitat specialist species under different grazing pressure. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Fig 2 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 2 Mean values (min-max and ±SE) of main parameters of orthopteran assemblages under different grazing pressure. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Fig 1 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 1 Location and land use-changes of the studied sites (G: grazed; G–A: grazing-abandoned; M–G: moderately grazed; U–G: ungrazed). Letters to the left of the arrow indicate land use in 2012 and 2013; letters to the right of the arrow indicate land use in 2014, 2015 and 2016.
Fig 5 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 5 Mean values (min-max and ±SE) of relative frequency of geophilic and vegetation structure-dependent species under different grazing pressure. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Fig 3 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 3 PCoA ordination (sum of all eigenvalues: 20.008, similarity index: correlation) based on Orthoptera data. The different years are marked by A, B, C, D and E (A: 2012, B: 2013, C: 2014, D: 2015 and E: 2016; e.g. 1-A: site 1 in 2012, 2-B: site 2 in 2013, C-C: control site in 2014).
Fig 7 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 7 CCA ordination based on Orthoptera data and environmental parameters (VCOV: total vegetation cover; BSOIL: percentage of bare soil; VH: height of the vegetation). Abbreviations of species names: Acr ins: Acrotylus insubricus; Acr ung: Acrida ungarica; Ail tha: Aiolopus thalassinus; Cal bar: Calliptamus barbarus; Cal ita: Calliptamus italicus; Cel var: Celes variabilis; Cho apr: Chorthippus apricarius; Cho big: Chorthippus biguttulus; Cho bru: Chorthippus brunneus; Cho mol: Chorthippus mollis; Doc bre: Dociostaurus brevicollis; Euc dec: Euchorthippus declivus; Euc pul: Euchorthippus pulvinatus; Gam gla: Gampsocleis glabra; Mon mon: Montana montana; Myr mac: Myrmeleotettix maculatus; Oed cae: Oedipoda caerulescens; Oed dec: Oedaleus decorus; Omo hae: Omocestus haemorrhoidalis; Omo min: Omocestus minutus; Omo pet: Omocestus petraeus; Omo ruf: Omocestus rufipes; Pla alb: Platycleis albopunctata; Sph cae: Sphingonotus caerulans; Ste fis: Stenobothrus fischeri; Ste lin: Stenobothrus lineatus; Ste nig: Stenobothrus nigromaculatus.
Fig 6 from: Kenyeres Z (2018) Effects of grazing on orthopteran assemblages of Central-European sand grasslands. Journal of Orthoptera Research 27(1): 23-33. https://doi.org/10.3897/jor.27.15033
Fig 6 Mean values (min-max and ±SE) of vegetation cover and vegetation height on the studied sites. Significant (p<0.05) differences detected by Mann-Whitney U test are indicated by different letters.
Fig. 4 in A remarkable sand-dwelling fish assemblage from central Amazonia, with comments on the evolution of psammophily in South American freshwater fishes
Fig. 4. The minute and translucent Stauroglanis gouldingi (not preserved) poised on the sandy stream bottom.
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