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22,710 results for “Plants for planting”
Figure 10 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 10. The lectotype of Ixora cuneifolia Roxb. Icones Roxburghianae 1785 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 6 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 6. The lectotype of Chrysophyllum acuminatum Roxb., replaced synonym of Chrysophyllum roxburghii G.Don. Icones Roxburghianae 2041 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 9 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 9. The lectotype of Randia racemosa Roxb., basionym of Hypobathrum racemosum (Roxb.) Kurz. Icones Roxburghianae 1207 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 2 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 2. The lectotype of Arum cuspidatum Roxb., replaced synonym of Arisaema roxburghii Kunth. Icones Roxburghianae 1657 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 13 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 13. The lectotype of Paederia erecta Roxb. Icones Roxburghianae 2196 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 7 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 7. The lectotype of Ambrosina retrospiralis Roxb., basionym of Cryptocoryne retrospiralis (Roxb.) Kunth. Icones Roxburghianae 1292 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure 5 in FROM ACACIA TO ZIZIPHUS: PLANT NAMES COMMEMORATING THE BOTANIST WILLIAM ROXBURGH
Figure 5. The lectotype of Quercus lanceifolia Roxb., and hence Castanopsis lanceifolia (Oerst.) Hickel & A.Camus. Icones Roxburghianae 2384 in the collection of the Royal Botanic Gardens, Kew. Reproduced with the permission of the Board of Trustees of the Royal Botanic Gardens, Kew.
Figure. 3 in Niche separation between the cosmopolitan species Drosophila melanogaster and the tropical Asian species Drosophila ananassae based on larval host-plant species
Figure. 3. Statistical interaction between Drosophila species and larval host plant in determining the number of male flies eclosing in the present experiment. Blue circles represent replicates for Drosophila ananassae and Drosophila melanogaster when raised on cucumberfruit (Averrhoa bilimbi). Red circles indicate replicates where D. ananassae or D. melanogaster were raised on banana (Musa sp.). The number of male flies eclosing from each replicate are presented as squareroot transformed data (variable: TFlies), since the transformed data were used in the ANOVA to determine the statistical significance of this statistical interaction. Da. = Drosophila ananassae, Dm.= Drosophila melanogaster.
Figure 2 in Niche separation between the cosmopolitan species Drosophila melanogaster and the tropical Asian species Drosophila ananassae based on larval host-plant species
Figure 2. Number of Drosophila ananassae and Drosophila melanogaster eclosing in the present experiment, pooling across fruit types. Da. = Drosophila ananassae, Dm.= Drosophila melanogaster.
Figure 1 in Niche separation between the cosmopolitan species Drosophila melanogaster and the tropical Asian species Drosophila ananassae based on larval host-plant species
Figure 1. Number of male flies eclosing from cucumberfruit (Averrhoa bilimbi) vs. banana (Musa species), pooled across Drosophila Species.
Fig. 2 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans
Fig. 2. The efficacy of the natural components against E. tenella sporozoites. The viability of sporozoites was determined at various concentrations of the compounds that showed effectiveness at 100 μM. The half maximal inhibitory concentration (IC50) value was determined from the approximate curves obtained from these results. SPZ: sporozoite.
Fig. 1 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans
Fig. 1. Direct effects of the natural components derived from alpine plants on E. tenella sporozoites. The viability of sporozoites treated with each natural component derived from alpine plants or lasalocid (positive control) with the viability of the DMSO-treated group set as 100%. The final concentration was 100 μM for the natural components, and 1 μM for lasalocid. SPZ: sporozoite; Las: lasalocid. Outliers were tested using Thompson's test (p <0.05), and the student's t-test was utilized to compare the data with the DMSO-treated group as a control (**p <0.01, ***p <0.001, ****p <0.0001).
Fig. 3 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans
Fig. 3. Confirmation of the active compounds using commercially available compounds and their efficacy. (A) The viability of sporozoites treated with each commercially available compound or lasalocid (positive control) was compared to the viability of the DMSO-treated group, which was set as 100%. The final concentration was 100 μM for the synthetic compounds, and 1 μM for lasalocid. SPZ: sporozoite, Las: lasalocid. The student's t-test was used for the comparisons (****p <0.0001) without outliers, as tested using Thompson's test (p <0.05). (B) The viability of sporozoites was determined at each concentration of the synthetic compounds that showed effectiveness at 100 μM. The half maximal inhibitory concentration (IC50) value was determined by approximating the curves obtained from the results.
Fig. 4 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans
Fig. 4. The inhibitory effects of the natural components derived from alpine plants on sporozoite cell invasion. The invasion rate of sporozoites treated with each natural component derived from alpine plants or lasalocid (positive control) with the viability of the DMSO-treated group set as 100%. Each compound was used at its maximum non-toxic concentration. Las: lasalocid. The student's t-test was utilized to compare the data with the DMSO-treated group as a control (**p <0.01, ***p <0.001, ****p <0.0001). Outliers were identified and removed using Thompson's test (p <0.05).
Fig. 8. Plant cuticles and tracheids from the Ivanye Zolote section. GIUS 4−3592. A. Cosmochlaina verrucosa Edwards, 1986 in Palynology and microfacies of Lower Devonian mixed carbonate-siliciclastic deposits in Podolia, Ukraine
Fig. 8. Plant cuticles and tracheids from the Ivanye Zolote section. GIUS 4−3592. A. Cosmochlaina verrucosa Edwards, 1986; IZ−7 sample. B. Nematothallus sp.; IZ−7 sample. C. Nematothallus sp.; IZ−1 sample. D–G. Nematothallus? like structures. D, E. IZ−6 sample. F, G. IZ−1 sample. H–I. Porcatitubulus annulatus Burges and Edwards, 1991. H. IZ−5 sample. I. IZ−4 sample. J. Laevitubulus sp.; IZ−1 sample. K. Porcatitubulus annulatus Burges and Edwards, 1991; IZ−5 sample.
Figure 2 in The structure and composition of the woody plant communities of Majete Wildlife Reserve, Malawi
Figure 2. Typical examples of the plant communities in Majete Wildlife Reserve; A, riparian woodland (Rw); B, grassland (Gr); C–D, shrublands and woodlands (SW); E, transitional woodland (Tw); and F, miombo (M). Photo credits: W.A. Nieman.
Figure 5 in Motivations and contributions of volunteer groups in the management of invasive alien plants in South Africa's Western Cape province
Figure 5. Challenges (n = 56) faced by individual volunteers in the management of invasive alien plant management in Western Cape, South Africa.
Figure 4 in Motivations and contributions of volunteer groups in the management of invasive alien plants in South Africa's Western Cape province
Figure 4. Reasons for initial engagement (n = 71) in volunteering and the current motivations (n = 86) for volunteers to be involved in the management of invasive alien plant species in Western Cape, South Africa.
Figure 2 in Motivations and contributions of volunteer groups in the management of invasive alien plants in South Africa's Western Cape province
Figure 2. Motivations (n = 35) for forming volunteer groups that remove alien invasive plants in Western Cape, South Africa.
Figure 1 in Motivations and contributions of volunteer groups in the management of invasive alien plants in South Africa's Western Cape province
Figure 1. Identified volunteer groups (52) in Western Cape of South Africa. Groups that participated in the survey (26) are indicated by circles that also show group sizes (individual members per group). Groups that did not participate in the survey are indicated by blue circles. The green area on the map represents the fynbos biome.
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
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.