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FIGURE 2 in Molecular taxonomy of two sympatric sibling species of the pollenbeetle genus Meligethes (Coleoptera: Nitidulidae)
FIGURE 2. Neighbor Joining based on K2P pair wise distances matrix for COII. Refer to Table 1 for specimens acronyms. In parentheses bootstrap values scored for the NJ analysis based on the uncorrected p distance values.
FIGURE 1 in Molecular taxonomy of two sympatric sibling species of the pollenbeetle genus Meligethes (Coleoptera: Nitidulidae)
FIGURE 1. Neighbor Joining based on K2P pair wise distances matrix for COI. Refer to Table 1 for specimens acronyms. In parentheses bootstrap values scored for the NJ analysis based on the uncorrected p distance values.
Figure 1 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 1. Map of South America and location of the Lagoa do Peixe National Park (LPNP) and study sites sampled in southern Brazil in 2008 and 2009.
Figure 4 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 4. Sex ratio for Austrolebias minuano (A) and Cynopoecilus fulgens (B) sampling in temporary ponds of Lagoa do Peixe National Park, southern Brazil, in 2008 and 2009.
Figure 5 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 5. Length–weight relationship for Austrolebias minuano (A) and Cynopoecilus fulgens (B) sampled in temporary ponds of Lagoa do Peixe National Park, southern Brazil, in 2008 and 2009.
Figure 6 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 6. Condition factor (K) ± SE of Austrolebias minuano (A) and Cynopoecilus fulgens (B) sampled in temporary ponds of Lagoa do Peixe National Park, southern Brazil, in 2008 and 2009.
Figure 2 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 2. Mean abundances ± SE of Austrolebias minuano (A) and Cynopoecilus fulgens (B) sampled in temporary ponds of Lagoa do Peixe National Park, southern Brazil, in 2008 and 2009.
Figure 3 in Abundance variations and life history traits of two sympatric species of Neotropical annual fish (Cyprinodontiformes: Rivulidae) in temporary ponds of southern Brazil
Figure 3. Mean standard length (LS) ± SE of Austrolebias minuano (A) and Cynopoecilus fulgens (B) sampled in temporary ponds of Lagoa do Peixe National Park, southern Brazil, in 2008 and 2009.
Figure 2 in Differentiated use of pollen sources by two sympatric species of oil-collecting bees (Hymenoptera: Apidae)
Figure 2. Pollen types used by Centris analis and Centris tarsata in larval provision. (A) Heteropterys sp. (polar view); (B) Solanum lycocarpum (polar view); (C) Banisteriopsis malifolia (polar view); (D) Byrsonima sp. (equatorial view); (E) Senna sp1 (equatorial view) and (F) Machaerium sp. (equatorial view).
Figure 1 in Spatial niche variation in two sympatric species of Bokermannohyla (Anura: Hylidae) in southeastern Brazil
Figure 1. Map showing the location of the RPPN Santuário do Caraça and the three streams where we sampled microhabitat use by Bokermannohyla nanuzae and Bokermannohyla martinsi.
Figure 2 in Comparisons in nesting biology of two sympatric carpenter bee species (Apidae: Xylocopini)
Figure 2. Average frequency of pollen collecting flights, nectar collecting flights and nectar dehydration performed by Xylocopa ordinaria and Xylocopa frontalis regarding the wet (A, C) and dry (B, D) seasons and the time of the day.
Figure 8 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 8. Differences in food preference for the two Ligia species [Ligia occidentalis (LO): F (4,53.45) = 15.918, p = 0.0001; Ligia pallasii (LP): F (4,53,45) = 15.928, p = 0.0004] as shown for mean dry weight consumed for each food type (error bars are ± 1 SE). Changes in weight of the different food types without isopods (none: F (4,22.15) = 0.699, p = 0.601) show minimal changes in weight possibly because of microbial activity. Values of p are based on analysis of variance. Letters above bars indicate significant differences among means (Post hoc Tukey tests).
Figure 6 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 6. Results of mesocosm experiments show that all treatments containing Ligia showed a significant decrease in dry weight of algal biomass compared with a control (none). The reduction in algal biofilm caused by Ligia pallasii (LP) treatment was significantly lower than that by either the Ligia occidentalis (LO) treatment or the combination of the two species (LO+LP). Letters above bars indicate significant differences among means (Post hoc Tukey tests).
Figure 5 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 5. Temperature records at Mussel Point cave (A) and Bodega Harbor (B) represented as mean temperature per month (average) and the monthly average of the daily maximum (max) and minimum (min) temperatures.
Figure 4 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 4. Monthly survey of Ligia pallasii at Mussel Point from March 2007 to December 2010. Overall abundance is represented as mean number of individuals per square metre and is composed of numbers from five different size classes (see key).
Figure 3 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 3. Monthly survey of Ligia occidentalis at Bodega Harbor from March 2007 to December 2010. Overall abundance is represented as mean number of individuals per square metre and is composed of numbers from four different size classes (see key).
Figure 2 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 2. Relative abundance of Ligia occidentalis (LO) and Ligia pallasii (LP) along the surveyed coastline (x axis left to right represents latitudinal coordinates of sampling sites from south to north). LO showed slight but not significant decline in abundance towards the northern range of the distribution Spearman's ρ – 0.0863, p <|ρ| = 0.3680. LP showed a small but significant decline towards the southern range limit (positive correlation with increasing latitude Spearman's ρ 0.5499, p <|ρ| = 0.0001. Lines within sites mark area of range overlap (solid line range limit of species in plot, dashed line range limit of other Ligia species).
Figure 1 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 1. Ligia occidentalis (A) and Ligia pallasii (B, C) can be distinguished by the distance between the eyes and the shape of the caudal peduncle of the uropod. Sexual dimorphism is only present in L. pallasii (B, female; C, male). All scale bars represent 10 mm. Photos: J. Sones.
Figure 7 in Distribution, habitat and food preferences of sympatric high intertidal isopod species Ligia occidentalis and Ligia pallasii (Ligiidae: Oniscidea)
Figure 7. Feeding preferences (mean rank ± 1 SE) of Ligia pallasii and Ligia occidentalis for different species of algal wrack (Nereocystis, Costaria, Ulva, Mazaella and Fucus); n = 20 (L. pallasii), 19 (L. occidentalis). Different letters indicate significant differences in rank of pairwise comparisons after Bonferoni corrections.
Figure 3 in Egg production of two sympatric species of Hyalella Smith, 1874 (Crustacea, Amphipoda, Dogielinotidae) in aquaculture ponds in southern Brazil
Figure 3. Mean ± standard error of fecundity in each season. Only females carrying eggs (stage I, II and III) were considered in the analysis. Bars with at least one letter in common did not differ statistically (analysis of variance and Bonferroni; α = 0.05). Hyalella pleoacuta (A) and H. castroi (B).
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Allen Brain Atlas
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
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OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.