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1,014 results for “TIGER”
Figure 3 in Ecological niche overlap of two allopatric karst-adapted tiger geckos (Goniurosaurus) from northern Vietnam: microhabitat use and implications for conservation
Figure 3. Microhabitat characters of Goniurosaurus huuliensis and Goniurosaurus luii. (a) Air temperature; (b) substrate surface temperature; (c) animal temperature; (d) relative air humidity; (e) substrate angle; (f) occupied height; (g) canopy coverage; (h) elevation.
Figure 2 in Ecological niche overlap of two allopatric karst-adapted tiger geckos (Goniurosaurus) from northern Vietnam: microhabitat use and implications for conservation
Figure 2. (a) Karst mountain inhabited by Goniurosaurus huuliensis; (b) Microhabitat of Goniurosaurus luii; (c) G. huuliensis; and (d) G. luii on rock substrate. (Photographed by Hai N. Ngo.)
Figure 1 in Ecological niche overlap of two allopatric karst-adapted tiger geckos (Goniurosaurus) from northern Vietnam: microhabitat use and implications for conservation
Figure 1. Geographic distribution of Goniurosaurus huuliensis (violet circles enclosed by a violet line) and Goniurosaurus luii (pink triangles – northern Vietnam; pink squares – southern China – enclosed by a pink line). The orange square represents the distribution of another tiger gecko species, namely Goniurosaurus araneus, in China.
Figure 7 in Ecological niche overlap of two allopatric karst-adapted tiger geckos (Goniurosaurus) from northern Vietnam: microhabitat use and implications for conservation
Figure 7. Anthropogenic impacts in natural habitats of Goniurosaurus huuliensis and Goniurosaurus luii: (a) quarrying for cement production; (b) timber logging. (Photographed by Hai N. Ngo.)
Formation of c-C6H5CN ice using the SPACE TIGER experimental setup
<p>Benzonitrile (c-C6H5CN) has been recently detected in cold and dense regions of the interstellar medium (ISM), where it has been used as a signpost of a rich aromatic organic chemistry that might lead to the production of polycyclic aromatic hydrocarbons (PAHs).</p> <p>One possible origin of this benzonitrile is interstellar ice chemistry involving benzene (c-C6H6) and nitrile molecules (organic molecules containing the −C≡N group). We have addressed the plausibility of this c-C6H5CN formation pathway through laboratory experiments using the SPACE TIGER experimental setup.</p> <p>We have irradiated c-C6H6:CH3CN ice mixtures with 2 keV electrons (Experiments 3-5) and Ly-alpha photons (Experiment 6), and compared the results with those obtained after 2 keV electron irradiation of c-C6H6 (Experiment 1) and CH3CN (Experiment 2) ices. In addition, we have also irradiated H2O:c-C6H6:CH3CN (Experiments 7 and 8), and CO:c-C6H6:CH3CN (Experiments 9 and 10) ice mixtures with both, 2 keV electrons (Experiments 7 and 9) and Ly-alpha photons (Experiments 8 and 10). </p> <p>The results of these experiments are presented in</p> <table summary="Additional metadata"> <tbody> <tr> <td><a href="https://doi.org/10.48550/arXiv.2210.03827">https://doi.org/10.48550/arXiv.2210.03827</a></td> </tr> </tbody> </table>
Seagrass and tiger shark data
<p>Seagrass conservation is critical for mitigating climate change due to the large stocks of carbon they sequester in the seafloor. However, effective conservation and its potential to provide nature-based solutions to climate change is hindered by major uncertainties regarding seagrass extent and distribution. Here, we describe the characterization of the world's largest seagrass ecosystem, located in The Bahamas. We integrate existing spatial estimates with an updated empirical remote sensing product and perform extensive groundtruthing of the seafloor with 2,542 diver surveys across remote sensing tiles. We also leverage seafloor assessments and movement data obtained from instrument-equipped tiger sharks, which have strong fidelity to seagrass ecosystems, to augment and further validate predictions. We report a consensus area of at least 66,000 km<sup>2</sup> and up to 92,000 km<sup>2</sup> of seagrass habitat across The Bahamas Banks. Sediment core analysis of stored organic carbon further confirmed the global relevance of the blue carbon stock in this ecosystem. Data from tiger sharks proved important in supporting mapping and groundtruthing remote sensing estimates. This work provides evidence of major knowledge gaps in the ocean ecosystem, the benefits in partnering with marine animals to address these gaps, and underscores support for rapid protection of oceanic carbon sinks.</p>
Panzer VI Tiger War Tank
War Tank modeled and textured in a day, in Blender. Source: Objaverse 1.0 / Sketchfab
Tiger Seal/Chop
Personal seal, or chop. Incsribed with: Huasheng, Peanut Source: Objaverse 1.0 / Sketchfab
FIGURES 5–8. Pericaliella, male genitalia. 5–6, P in Two new tiger-moth species from Afrotropics with reviews of genera Pericaliella and Monstruncusarctia (Lepidoptera, Noctuoidea: Erebidae, Arctiinae)
FIGURES 5–8. Pericaliella, male genitalia. 5–6, P. melanodisca, Uganda, Kibale, 7–8, P. popoudinae sp. n., holotype, Rwanda, Butare. 5, 7, general view, 6, 8, aedeagus.
FIGURES 1–4 in Two new tiger-moth species from Afrotropics with reviews of genera Pericaliella and Monstruncusarctia (Lepidoptera, Noctuoidea: Erebidae, Arctiinae)
FIGURES 1–4. Pericaliella and Monstruncusarctia spp., males. 1, P. melanodisca, Uganda, Kibale; 2, P. popoudinae sp. n., holotype, Rwanda, Butare; 3, M. aurantiaca, Guinea, Kindia, 4, M. anikini sp. n., Uganda, Kibale.
FIGURES 9–12. Monstruncusarctia, male genitalia. 9, 11, M in Two new tiger-moth species from Afrotropics with reviews of genera Pericaliella and Monstruncusarctia (Lepidoptera, Noctuoidea: Erebidae, Arctiinae)
FIGURES 9–12. Monstruncusarctia, male genitalia. 9, 11, M. aurantiaca, Guinea, Kindia, 10, 12, M. anikini sp. n., Uganda, Kibale. 9-10, general view, 11-12, aedeagus.
Successful conservation translocation: Population dynamics of tiger recovery in Panna Tiger Reserve, Central India
<p>Tiger (<em>Panthera tigris</em>) is an indicator species of ecological health and conservation efforts. Due to excessive poaching, the tiger was locally extinct in Panna Tiger Reserve, central India. Subsequent successful reintroduction efforts have brought the species back from the verge of extinction and have demonstrated the success of conservation translocations in response to such critical situations.</p> <p>To understand the demographic characteristics of the tigers reintroduced to Panna Tiger Reserve, we used an ensemble approach of different sampling techniques and direct observations from a long-term data-set spanning more than 10 years. We evaluated different demographic indicators (population status, growth rate, mean litter size, inter-birth interval, and survival probability).</p> <p>Since reintroduction in 2009, 18 females have recruited 120 cubs from 45 litters. This led to 59 individuals in 2021 with a growth rate of ~26%. The mean litter size was 2.66 (SE 0.1), and the inter-birth interval was 19.16 months (SE 0.5). The high survival rate of the reintroduced population (0.82±0.2) helped to achieve the success of reintroduction. We observed non-constant mortality trajectories for both sexes (higher survival probabilities for females) with a moderately higher risk of death in younger (<1 year) and older (>10 years) individuals.</p> <p>Our results showed the effectiveness of translocation and conservation efforts. The recovered population can be used as a founder for augmentation in other recovering tiger populations. A long-term tiger-centric management plan should be implemented in the area adjacent to Panna Tiger Reserve to conserve and secure the habitat of the entire landscape for the long-term survival of the reintroduced population in a metapopulation framework.</p>
FIGURES 9–20 in New or rare Madagascar tiger beetles-17. Description of Pogonostoma (Microstenocera) noheli sp. nov. and redescription of P. (M.) flavomaculatum W. Horn (Coleoptera: Cicindelidae)
FIGURES 9–20. Pogonostoma (Microstenocera) noheli sp. nov. from type locality. 9––head, ♂, HT (SDEI); 10––mandibles, ♂, PT (CCJM); 11––galea with lacinia, ♂, HT; 12–13––labrum: 12––♂, HT; 13––♀, AT (CJVB); 14–20––aedeagi: 14––PT (CCJM); 15––ditto, dorsal view; 16––PT (CJVB); 17––ditto, ventral view; 18–19––PT (CJVB); 20––apex, HT (SDEI). Bars= 1 mm.
FIGURES 1–8 in New or rare Madagascar tiger beetles-17. Description of Pogonostoma (Microstenocera) noheli sp. nov. and redescription of P. (M.) flavomaculatum W. Horn (Coleoptera: Cicindelidae)
FIGURES 1–8. Pogonostoma (Microstenocera) noheli sp. nov. from type locality. 1–2––habitus: 1—♂, HT, 7.3 mm (SDEI); 2—♀, AT, 7.5 mm (CJVB); 3–4––elytron: 3—♂, HT; 4––♀, AT; 5–6––pronotum: 5––♂, HT; 6––♀, AT; 7–8––elytral apices: 7––♂, HT; 8––♀, AT. Bars = 1 mm.
FIGURES 31–44 in New or rare Madagascar tiger beetles-17. Description of Pogonostoma (Microstenocera) noheli sp. nov. and redescription of P. (M.) flavomaculatum W. Horn (Coleoptera: Cicindelidae)
FIGURES 31–44. Pogonostoma (Microstenocera) flavomaculatum W. Horn. 31––head, ♂, Andasibe-Mantadia (CCJM); 32– 33––maxillae: 32––lacinia, ♂, HT (SDEI); 33––lacinia and galea, ♂, Andasibe-Mantadia (CJVB); 34–36––labrum: 34––♂, HT (SDEI); 35––♂, Andasibe-Mantadia (CJVB); 36––♀, ibid. (CMTD); 37–43––aedeagi: 37––ibid., CMTD); 38–– ibid. (CCJM); 39––ditto, ventral view; 40–43––ibid.(CJVB); 44––original labels of HT (SDEI). Bars= 1 mm.
FIGURES 21–30 in New or rare Madagascar tiger beetles-17. Description of Pogonostoma (Microstenocera) noheli sp. nov. and redescription of P. (M.) flavomaculatum W. Horn (Coleoptera: Cicindelidae)
FIGURES 21–30. Pogonostoma (Microstenocera) flavomaculatum W. Horn. 21–22––habitus: 21––♂, HT (SDEI); 22––♂, Andasibe-Mantadia (CMTD); 23–24––elytral apices: 23––♂, ibid. (CCJM); 24––♀, ibid. (CMTD); 25–27––elytron: 25––♂, HT (SDEI); 26––♀, Andasibe-Mantadia (CCJM); 27––♂, apex of right elytron, HT (SDEI); 28–30––pronotum: 28––♀, Andasibe-Mantadia (CMDT); 29––♂, ibid. (CJVB); 30––♂, HT (SDEI). Bars= 1 mm.
Supplementary material 1 from: Assmann T, Boutaud E, Buse J, Gebert J, Drees C, Friedman A-L-L, Khoury F, Marcus T, Orbach E, Renan I, Schmidt C, Zumstein P (2018) The tiger beetles (Coleoptera, Cicindelidae) of the southern Levant: from cybertaxonomy to conservation biolog. ZooKeys 734: 43-103. https://doi.org/10.3897/zookeys.734.21989
TIGER BEETLE ID : Disclaimer of warranties. You expressly understand and agree that your use of the app "TIGER BEETLES ID" is at your sole risk and that the app is provided "as is" and "as available" without warranty of any kind from the authors.
FIGURE 2 in The Asian tiger mosquito, Aedes (Stegomyia) albopictus (Skuse), a vector of dengue, chikungunya and zika viruses, reaches Portugal (Diptera: Culicidae)
FIGURE 2. Portuguese Aedes albopictus females seeking human blood. Note characteristic scutal white stripe, distinct silvery-white scales on the maxillary palpi and tarsi, as well as narrow scales over the wing root and silvery-white basolateral abdominal tergal markings.
FIGURE 1 in The Asian tiger mosquito, Aedes (Stegomyia) albopictus (Skuse), a vector of dengue, chikungunya and zika viruses, reaches Portugal (Diptera: Culicidae)
FIGURE 1. Distribution of Aedes albopictus in the Iberian Península. In green, distribution in Spain according to Collantes et al. (2016). In red, highlighted by arrow, new occurrence in Portugal.
FIGURE 3 in The Asian tiger mosquito, Aedes (Stegomyia) albopictus (Skuse), a vector of dengue, chikungunya and zika viruses, reaches Portugal (Diptera: Culicidae)
FIGURE 3. Biting activity of Ae. albopictus assessed by human-bait catches. Specimens arriving to bite were captured every 15 minutes to avoid recapture. The x axis is a timeline of 15-minute intervals; the y axis is an average of the three days of sampling.
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