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Figure 2 in The range dynamics of a cactophilic Drosophila species under climate change scenarios

Figure 2. Occurrence points used for ecological niche modeling are shown in red. Squares equal approximately 2 decimal degrees and the background image on thmap shows the elevational structure of Brazil.

Figure 1 in The range dynamics of a cactophilic Drosophila species under climate change scenarios

Figure 1. Approximate distribution of D. gouveai (green area) showed Caatinga and Cerrado domains and the localities sampled for the species (based on Moraes et al., 2009), descriptive statistics (n, number of individuals; H, the number of haplotype; H d, haplotype diversity; pi, nucleotide diversity) and median joining network of 48 individuals of D. gouveai. All statistics based on nucleotide sequences were adopted from Moraes et al. (2009). MIR: Pirapotanga; FOR: Morro do Forno; FUR: Furnas; CEU: Vale do Céu; CRI: Cristalina; FER: Fercal; PIR: Pirenópolis; SER: Serrinha; IBO: Ibotirama; BAX: Baxio.

Figure 4 in The range dynamics of a cactophilic Drosophila species under climate change scenarios

Figure 4. Last Interglacial, Last Glacial Maximum, Present (1960–1990), and the Future (2050 and 2070) predictions of the potential distribution of D. gouveai based on two thresholding approaches. Arrows shows very limited potential distribution of D. gouveai in 2050 and 2070. The abbreviations are defined as follows: LGM-Last Glacial Maximum, LIG-Last Interglacial. Additionally, specific climate models include LGM-cc (Community Climate System Model), LGM-me (MPI-ESM-P, General Circulation Models), and LGM-mr (Model for Interdisciplinary Research on Climate, Earth System version 2 for Long-term simulations).

Figure 3 in The range dynamics of a cactophilic Drosophila species under climate change scenarios

Figure 3. Isolation-by-distance of populations of D. gouveai based on mtDNA. Linear regression lines were drawn for all comparisons among populations (full line), and for populations not included MIR (dotted line).

opencc-by-4.0Dec 2009View details →

Figure 1 in Victoriasquilla poorei, a new genus and species of mantis shrimp from southern Australia, and a range extension for Hadrosquilla edgari Ahyong, 2001 (Crustacea: Stomatopoda: Nannosquillidae)

Figure 1. Victoriasquilla poorei gen et sp. nov., male holotype, TL 17 mm (NMV J53108). A, anterior cephalothorax. B, right eye, lateral view. C, right antennal protopod, lateral view. D, right raptorial claw, lateral view. E, thoracic somites 5–8, right dorsal view. F–H, right pereopods 1–3, respectively, posterior view. I, posterior abdomen, telson and right uropod, dorsal view. J, posterior abdomen and telson, right lateral view. K, right uropod, ventral view. L, telson, ventral view. Scale 1.0 mm

opencc-zeroMar 2020View details →

FIG. 1 in Sighting of Saccorhiza polyschides (Lightfoot) Batters (Phaeophyceae, Stramenopiles) in Algeria (Mediterranean Sea): an insight into range expansion routes

FIG. 1. — Mediterranean records of Saccorhiza polyschides (Lightfoot) Batters. The date is that of the sighting and, if unknown, that of the publication. TABLE 1. — Mediterranean records of Saccorhiza polyschides (Lightfoot) Batters. Records from the Alboran Sea, close to the Straits of Gibraltar, are not reported.

opencc-by-4.0Dec 2023View details →

High-power in-phase and anti-phase mode emission from linear arrays of resonant-tunneling-diode oscillators in the 0.4-to-0.8-THz frequency range - data

<div> <p>Experimental and simulation data from the paper "High-power in-phase and anti-phase mode emission from linear arrays of resonant-tunneling-diode oscillators in the 0.4-to-0.8-THz frequency range".</p> <p> </p> </div>

Fig. 9 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 9. The area of distribution of P. melas for 2050 at annual increment of the temperature measuring 0.03–0.05 ºC: for keys see Fig. 8

Fig. 4 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 4. Presumed range of P. fornicatus in 2050 at mean increase in average temperature to 2100 equaling 2.4 ºC: for keys see Fig. 2

Fig. 5 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 5. Predicted range of P. fornicatus in 2070 at mean increment of 2.4 ºC to 2100: for keys see Fig. 2 ASK BRIG

Fig. 10 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 10. Area of the distribution of P. melas in 2070 at annual increment of the temperature equaling 0.03–0.05 ºC: for keys see Fig. 8

Fig. 1 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 1. Analysis of the accuracy of the model of probable distribution: a – omission and Predicted Area for P. fornicatus: 1 – test data, 2 – training data, 3 – fraction of the initial data presented, 4 – predicted emission; b – trend of the operating curve AUC: 1 – test data, 2 – training data, 3 – random prediction

Fig. 8 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 8. Area of distribution of Pterostichus melas:in red the most suitable zones for living are indicated (80–100%), orange – 50–80%, yellow – 20–50%, green – less than 10%, dark blue – 0%

Fig. 3 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 3. Curves of dependence of the model of probable distribution of P. fornicatus on bioclimatic parameters: a – Bio11; along the abscissa axis – mean temperature of the coldest quarter of year; on the ordinate axis – index of suitability for the species, b – Bio14; on the abscissa axis – amount of precipitations in the driest month of the year; on the ordinate axis – index of suitability for the species, c – Bio 6; on the abscissa axis – minimum temperature

Fig. 2 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 2. Model of potential (probable) range of P. fornicatus assessed in Maxent software basing on the data of WorldClim: in red the most suitable areas for living are indicated (70–100%), orange – 50–70%, yellow – 20–50%, blue – 0%.

Fig. 6 in Changes in the range of Pterostichus melas and P. fornicatus (Coleoptera, Carabidae) on the basis of climatic modeling

Fig. 6. Statistical analysis of the obtained model of the probable distribution of P. melas: a – omission and Predicted Area for P. melas: 1 – test data, 2 – training data, 3 – fraction of the initial data which were predicted, 4 – predicted emission; b – trend of the operative curve AUC: 1 – test data, 2 – training data, 3 – random prediction

opencc-zeroJun 2024View details →

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Data from: Spring temperature predicts upstream migration timing of invasive Sacramento pikeminnow within its introduced range

<p>Rapid climate change and invasive species introductions threaten ecological communities across the globe. Freshwaters are particularly vulnerable and impacted, especially when these stresses coincide. We document the migration of an invasive piscine predator, the Sacramento pikeminnow (<em>Ptychocheilus grandis</em>), within its introduced range, the South Fork Eel River, California, USA. Snorkel surveys and temperature monitoring in 2015–2019 showed that pikeminnow migrate upstream during spring and early summer, with earlier migration in warmer years. We developed a statistical temperature model to forecast the timing and extent of upstream migration by pikeminnow under varying combinations of discharge and air temperature. Modeled river temperature increased with air temperature and downstream and decreased with discharge. In years with low discharge and high air temperature, we predict pikeminnow will move upstream earlier, increasing spatial and temporal overlap in their summer range with native fishes. Managing conditions that reduce pikeminnow co-occurrence with native fishes (i.e., decreasing river temperature) could increase the amount and duration of predator-free habitat for native fishes. We predict invasive pikeminnow will have larger impacts on invaded riverine communities with global warming and increasing drought severity. Knowledge of life history and phenology, for pikeminnow and other organisms, can guide effective management as conditions change and help to limit adverse impacts of introduced organisms on native species.</p>

opencc-zeroJun 2024View details →

Dataset: WisdomTree Target Range Fund (GTR) Stock Performance

This dataset provides historical stock market performance data for specific companies. It enables users to analyze and understand the past trends and fluctuations in stock prices over time. This information can be utilized for various purposes such as investment analysis, financial research, and market trend forecasting.

opencc-zeroJun 2024View details →

Dataset: Range Oncology Therapeutics Index ETF (CNCR) Stock Performance