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170 results for “Anole”
Anole ground level transects (Bisley and El Verde)
Transects are surveyed through the upper and lower cut plots at Bisley to determine the distribution and minimum abundance of anoles within and adjacent to the plots. Surveys began prior to cutting will continue seasonally (wet and dry) to document changes as the plots regenerate. One set of two transects has been established near the walkway towers in the 9 ha grid at El Verde. Each transect is 90 m long (wet 1989 and dry 1990) and 120 m long thereafter. Two transects, each 120 m long are established near the tower at Bisley. Survey methods and data recorded are the same for all transects, except that distance along the transect is recorded for cut plot transects only. Support for this work was provided by grants BSR-8811902, DEB-9411973, DEB-9705814 , DEB-0080538, DEB-0218039 , DEB-0620910 , DEB-1239764, DEB-1546686, and DEB-1831952 from the National Science Foundation to the University of Puerto Rico as part of the Luquillo Long-Term Ecological Research Program. Additional support provided by the University of Puerto Rico and the International Institute of Tropical Forestry, USDA Forest Service.
Anole treefall gap transects (Bisley and El Verde-H10 Gaps)
Transects were established through large recent treefall gaps to determine the relative abundance of different anole species at different distances from the center of the gap. Support for this work was provided by grants BSR-8811902, DEB-9411973, DEB-9705814 , DEB-0080538, DEB-0218039 , DEB-0620910 , DEB-1239764, DEB-1546686, and DEB-1831952 from the National Science Foundation to the University of Puerto Rico as part of the Luquillo Long-Term Ecological Research Program. Additional support provided by the University of Puerto Rico and the International Institute of Tropical Forestry, USDA Forest Service.
Anole Vertical Transects (tower data)
<p>Transects are conducted to note the vertical distribution and relative abundance of anole species. Data permit the calculation of average sighting distance for each species which is used in the final calculation of abundance.</p> Support for this work was provided by grants BSR-8811902, DEB-9411973, DEB-9705814 , DEB-0080538, DEB-0218039 , DEB-0620910 , DEB-1239764, DEB-1546686, and DEB-1831952 from the National Science Foundation to the University of Puerto Rico as part of the Luquillo Long-Term Ecological Research Program. Additional support provided by the University of Puerto Rico and the International Institute of Tropical Forestry, USDA Forest Service.
Anole Mark and Resight Study
The population distribution research area of the LEF LTER is designed to gather information on the distribution and abundance of key plant and animal species within the forest under different disturbance regimes. Multiple mark and resight studies were conducted to determine the population density of Anolis stratulus at one undisturbed forest site and one site in a partially regenerated treefall gap. Tower surveys were conducted in order to access individuals in the forest canopy.</p> Support for this work was provided by grants BSR-8811902, DEB-9411973, DEB-9705814 , DEB-0080538, DEB-0218039 , DEB-0620910 , DEB-1239764, DEB-1546686, and DEB-1831952 from the National Science Foundation to the University of Puerto Rico as part of the Luquillo Long-Term Ecological Research Program. Additional support provided by the University of Puerto Rico and the International Institute of Tropical Forestry, USDA Forest Service.
Anole Grid Study
Transects 60 m long are conducted at alternate points in the 9 ha grid at El Verde. Transects 80 m long are conducted at alternate points at the Bisley Grid in watersheds #1 and #2. Data are used to support the GIS database.</p> Support for this work was provided by grants BSR-8811902, DEB-9411973, DEB-9705814 , DEB-0080538, DEB-0218039 , DEB-0620910 , DEB-1239764, DEB-1546686, and DEB-1831952 from the National Science Foundation to the University of Puerto Rico as part of the Luquillo Long-Term Ecological Research Program. Additional support provided by the University of Puerto Rico and the International Institute of Tropical Forestry, USDA Forest Service.
Fig. 3 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 3. Male dewlap of Anolis poei sp. nov. (holotype, QCAZ 3449, A; paratype, QCAZ 3455, B); A. otongae (QCAZ 4661, C; QCAZ 11791, D); and A. gemmosus (QCAZ 4385, E; QCAZ 4352, F; QCAZ 9452, G; QCAZ 11850, H). Photographs by L. Bustamante (A), O. Torres-Carvajal (B, C, D, E, F, H), and S. R. Ron (G).
Fig. 3 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 3. Ontogenetic transformation of color and pattern in Andinophryne olallai from Río Manduriacu, Imbabura Province, Ecuador. (A) Froglet (11 mm SVL; in situ), (B) Froglet (15.1 mm SVL; in situ), (C) Juvenile (26.3 mm SVL; in situ), (D) Juvenile (28.1 mm SVL; in situ), (E) Adult (44.6 mm SVL; ex situ), (F) Adult (53.3 mm SVL; in situ). Note the progressive ontogenetic change in dorsal patterning from heavily mottled to no pattern; lack of parotoid glands and tubercles along the flank to presence of conspicuous parotoid glands and tubercles along the flank; a darkening of color from copper, tan, and white to dark brown; and iris color change from vibrant crimson to copper-orange.
Fig. 9 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 9. Distribution of Anolis gemmosus (triangles), A. otongae (circles) and A. poei sp. nov. (squares) in Ecuador.
Fig. 8 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 8. Phylogeny of the "western Dactyloa clade" sensu Castañeda and de Queiroz (2011), which is part of the aequatorialis series of Castañeda and de Queiroz (2013), and representatives of the heterodermus series (A. euskalerri- ari), punctatus series (A. transversalis), roquet series (A. lu- ciae), latifrons series (A. agassizi), and a non-Dactyloa Anolis (A. occultus). The tree is a majority rule (50%) consensus tree of 72,000 trees obtained from a Bayesian analysis of the mitochondrial genes COI, ND2, and adjacent tRNAs, and the nuclear gene RAG1. Asterisks correspond to posterior probability values ≥ 0.99. Voucher information is presented in Castañeda and de Queiroz (2011) and Table 1.
Fig. 5 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 5. Distribution of Anolis gemmosus, A. otongae and A. poei sp. nov. along the first and second principal components axes.
Fig. 4. Part 2. A in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 4. Part 2. A. gemmosus: male (QCAZ 4352, I, J), male (QCAZ 4385, K, L), male (QCAZ 11849, M, N), and female (QCAZ 4393, O, P). All photographs by O. Torres-Carvajal, except A, M, N (S. R. Ron).
Fig. 1 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 1. Head of the holotype (QCAZ 3449) of Anolis poei sp. nov. in dorsal (top), ventral (middle), and lateral (bottom) views [Scale bar = 10 mm]. Photographs by F. Ayala-Varela.
Fig. 4. Part 1 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 4. Part 1. Five species of Anolis from western Ecuador. A. aequatorialis: male (QCAZ 11861, A) and female (QCAZ 3443, B); A. binotatus: male (QCAZ 3434, C, D); A. fasciatus: male (QCAZ 3450, E, F); A. otongae: male (QCAZ 11790, G) and female (QCAZ 11791, H).
Fig. 7 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 7. Anolis poei sp. nov. Adult female (SVL = 46.47 mm, QCAZ 3454, A, B), subadult female (SVL = 47.99 mm, QCAZ 3446, C, D), juvenile male (SVL = 26.85 mm, QCAZ 3453, E, F). Photographs by O. Torres-Carvajal.
Fig. 6 in A new Andean anole species of the Dactyloa clade (Squamata: Iguanidae) from western Ecuador
Fig. 6. Tongue of Anolis poei sp. nov., subadult male (QCAZ 3455, top); A. gemmosus, adult male (QCAZ 4347, middle); A. otongae, adult male (QCAZ 4661, bottom). Photographs by S. R. Ron (top), O. Torres-Carvajal (middle, bottom).
Linked collectors and determiners for: UWIZM Anoles.
Natural history specimen data linked to collectors and determiners held within, "UWIZM Anoles". Claims or attributions were made on Bionomia by volunteer Scribes, <a href="https://bionomia.net/dataset/beae8840-4e3d-46d3-aa0b-4a60aaba0b49">https://bionomia.net/dataset/beae8840-4e3d-46d3-aa0b-4a60aaba0b49</a> using specimen data from the dataset aggregated by the Global Biodiversity Information Facility, <a href="https://gbif.org/dataset/beae8840-4e3d-46d3-aa0b-4a60aaba0b49">https://gbif.org/dataset/beae8840-4e3d-46d3-aa0b-4a60aaba0b49</a>. Formatted as a Frictionless Data package.
Urbanization drives habitat suitability of the invasive Cuban Knight Anole (<em>Anolis equestris</em>) in Florida, USA
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Data from: The genetic architecture of dewlap pattern in Hispaniola Anoles (Anolis distichus)
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Data from: Environmental variation influences genome evolution in Hispaniolan trunk anoles (<i>Anolis distichus</i>)
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A morphometric assessment of species boundaries in a widespread anole lizard (Squamata: Dactyloidae)
<p>Cryptic species - genetically distinct species that are morphologically difficult to distinguish - present challenges to systematists. Operationally, cryptic species are very difficult to identify and sole usage of genetic data or morphological data can fail to recognize evolutionarily isolated lineages. We use morphometric data to test species boundaries hypothesized with genetic data in the North Caribbean Bark Anole (<i>Anolis distichus</i>), a suspected species complex. We use univariate and multivariate analyses to test if candidate species based on genetic data can be accurately diagnosed. We also test alternate species delimitation scenarios with a model fitting approach that evaluates normal mixture models capable of identifying morphological clusters. Our analyses reject the hypothesis that the candidate species are diagnosable. Neither uni- nor multivariate morphometric data distinguish candidate species. The best supported model included two morphological clusters; however, these clusters were uneven and did not align with a plausible species divergence scenario. After removing two related traits driving this result, only one cluster was supported. Despite substantial differentiation revealed by genetic data, we recover no new evidence to delimit species and refrain from taxonomic revision. This study highlights the importance of considering other types of data along with molecular data when delimiting species.</p>
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