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opencc-by-4.0Jul 2017View details →

Fig. 4 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Fig. 4. Female Pine Snakes sometimes remain in their nests for several days after egg-laying is complete, perhaps protecting their clutch from being disrupted by other females that lay in the same nest.

opencc-by-4.0Jul 2017View details →

Fig. 2 in Stakeholder contributions to conservation of threatened Northern Pine Snakes (Pituophis melanoleucus, Daudin, 1803) in the New Jersey Pine Barrens as a case study

Fig. 2. Female Northern Pine Snakes dig their own nests in the New Jersey Pine Barrens, although in the southern part of their range they do not do so. They bend their neck such that the head forms a scoop capable of bringing sand out the entrance (Fig 2a). While digging their body is hidden below ground, and the dump pile of sand is visible (and serves to attract poachers; Fig 2b).

Figure 6 in Reproductive biology of Tylototriton yangi (Urodela: Salamandridae), with suggestions on its conservation

Figure 6. Habitat destruction of Tylototriton yangi in southern Yunnan Province, China. a) Coal mining site at Yangjie, Mengzi, Yunnan Province, China; b) illegal tin mining at the type locality of T. yangi in Gejiu, Yunnan, China; c) Deforestation and infrastructure constructions at the type locality of T. yangi in Gejiu, Yunnan, China. Photographs by Kai WANG.

Fig. 1 in Reproductive biology of Tylototriton yangi (Urodela: Salamandridae), with suggestions on its conservation

Fig. 1. Location of the study site (the type locality of Tylototriton yangi) at Gejiu, Honghe Prefecture, Yunnan Province, PR China. Numbered locations of potential breeding pools (abbreviated as PBP) are shown in yellow.

Fig. 5 in Reproductive biology of Tylototriton yangi (Urodela: Salamandridae), with suggestions on its conservation

Fig. 5. Developmental series from fertilized embryos to newly metamorphosed juvenile of Tylototriton yangi. Clockwise from the upper left: a) fertilized embryos of T. yangi; embryos sank to the bottom of water, and were not adhesive to plants, the bottom of the container, or to one another; b) newly hatched larvae with one pair of balancers 6-day post-hatch; c) larva 17-days post-hatch, in which the forelimbs became visible; d) larva 50-days post-hatch; e) larva 75-days post-hatch; f) pre-metamorphic larva 95-days post hatch; g) newly metamorphosed individual 115-day post hatch. Photographs by Kai WANG and Guangyu LI.

Fig. 4 in Reproductive biology of Tylototriton yangi (Urodela: Salamandridae), with suggestions on its conservation

Fig. 4. Pre-spermatophore courtship behavior pattern of Tylototriton yangi in captivity. Clockwise from top-left: a) male nudging the side of the female's head with his snout; b) male nudging the side of the female's body; c) male blocking female's path and beginning to fold his tail; and d) male fanning the tip of his tail toward the female's head. Photographs by Kai WANG.

Fig. 2 in Reproductive biology of Tylototriton yangi (Urodela: Salamandridae), with suggestions on its conservation

Fig. 2. Habitat in which Tylototriton yangi was found at the type locality of Gejiu. Examples of typical breeding pools are shown at the right corner (from left to right, PBP#17 and PBP#12), and positions of other pools are indicated by white arrows. Photographs by Kai WANG.

opencc-by-4.0Jun 2018View details →

Fig. 1 in Evaluation of reduced-risk insecticides to control chilli thrips (Thysanoptera: Thripidae) and conserve natural enemies on ornamental plants

Fig. 1. Mean percentage (± SEM) of Rhaphiolepsis indica foliage with Scirtothrips dorsalis feeding damage 42 days afer insecticide treatment. Different letters indicate significant differences between treatments using Tukey-Kramer HSD means comparison (P <0.05). Cyantraniliprole low (59.1 mL per 378.5 L) and cyantraniliprole high (236.6 mL per378.5 L).

Fig. 3. Spectrograms and oscillograms for Dendropsophus vraemi. A–B in The distribution and calls of Vraem' Treefrog, Dendropsophus vraemi (Caminer, Milá, Jansen, Fouquet, Venegas, Chávez, Lougheed, and Ron 2017), with comments on its conservation status

Fig. 3. Spectrograms and oscillograms for Dendropsophus vraemi. A–B: variations of the advertisement call; C: an aggressive call. A, B and C are call variations from a single male individual (CORBIDI 17894) recorded in the middle Apurimac basin.

Fig. 3 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil

Fig. 3. Breeding of Scinax alcatraz at São Paulo Zoo. a) A pair in amplexus. b) Eggs deposited in the water. c) Maintanance of tadpoles in plastic pots with filtered water. d) Post-metamorph individuals (SVL x=12.49 mm). Photos by Cybele Lisboa.

Fig. 6 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil

Fig. 6. Range of environmental conditions (relative humidity and air temperature) most favorable for reproduction of Scinax alcatraz in captivity.

Fig. 5 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil

Fig. 5. Correlation between breeding events of Scinax alcatraz and environmental conditions (a) relative humidity and (b) air temperature from August 2013 to December 2017. Pearson product-moment Correlation Coefficient: r = 0.323; p <0.001; N = 732.

Fig. 2 in The distribution and calls of Vraem' Treefrog, Dendropsophus vraemi (Caminer, Milá, Jansen, Fouquet, Venegas, Chávez, Lougheed, and Ron 2017), with comments on its conservation status

Fig. 2. Dorsolateral and ventral views of Dendropsophus vraemi in life. A–B: CORBIDI 17894 (SVL = 26.4 mm); C–D: CORBIDI 17895 (SVL = 26.1 mm); E–F: CORBIDI 21857 (SVL = 22.8 mm); G–H: CORBIDI 21858 (SVL = 22.9 mm).

Fig. 2 in Captive breeding program for Scinax alcatraz (Anura: Hylidae): introducing amphibian ex situ conservation in Brazil

Fig. 2. Laboratory colony of Scinax alcatraz at Sao Paulo Zoo. a) Aquariums for maintanance of juveniles and adults. b) Plastic cups with filtered water and submerged plants for refuge. Photos by Cybele Lisboa.

Fig. 1 in The distribution and calls of Vraem' Treefrog, Dendropsophus vraemi (Caminer, Milá, Jansen, Fouquet, Venegas, Chávez, Lougheed, and Ron 2017), with comments on its conservation status

Fig. 1. Geographic distribution map for Dendropsophus vraemi showing the type locality (green triangle; Caminer et al. 2017) and new localities in the middle and lower Apurimac basin (yellow circles), extending the range by 151 km to the northwest.

opencc-by-4.0Nov 2021View details →

Fig. 1 in Rapid endangerment of the lizard Podarcis pityusensis by an invasive snake demands an immediate conservation response

Fig. 1. Basic elements of the system. (A) Map showing the location of Ibiza island in relation to the nearest mainland areas in the Iberian Peninsula and northern Africa. (B) The endemic lacertid lizard, Podarcis pityusensis. (C) The invasive colubrid snake, Hemorrhois hippocrepis. Photos by: Javier Pleguezuelos (A), Juan M. Pleguezuelos (B), and Federico Rey (C).

opencc-by-4.0Oct 2021View details →

Fig. 3 in Advertisement calls of six glassfrog species in the Colombian Andes, and comments on priorities for future research and conservation

Fig. 3. Counts of glassfrog species for those with and without the call described, and categorized by: (A) IUCN conservation status categories; (B) Endemism or distribution range (see details in Materials and Methods); and (C) Occurrence in National Protected Areas.

opencc-by-4.0Oct 2021View details →

Fig. 2 in Advertisement calls of six glassfrog species in the Colombian Andes, and comments on priorities for future research and conservation

Fig. 2. Spectrograms (top) and oscillograms (bottom) of the described glassfrogs advertisement calls. All calls are displayed at Blackman window (length = 512) and 80% overlap, at the same frequency range, and all but S. punctulata and C. huilensis are displayed at the same temporal scale.

opencc-by-4.0Sep 2021View details →

Fig. 16 in The herpetofauna of Veracruz, Mexico: composition, distribution, and conservation status

Fig. 16. Exotic and invasive species. Originally, this invasive species, Eleutherodactylus planirostris, was documented in the state of Veracruz by García-Vinalay et al. (2020). This individual was photographed in Puerto de Veracruz, in the municipality of the same name. Photo by Madeleine Fernández Teco.