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394 results for “urban forest”
Fig. 5 in Diversity and microhabitat use of benthic invertebrates in an urban forest stream (Southeastern Brazil)
Fig. 5. Boxplot of the ecological descriptors calculated for each microhabitat type (litter, sand, and stone) with the one-way repeated measure ANOVA results and the Tukey pairwise post hoc test (letters). Different letters denote significant difference results (p <0.001).
Figs 1-3 in Diversity and microhabitat use of benthic invertebrates in an urban forest stream (Southeastern Brazil)
Figs 1-3. Sampled stretches of the Tijuca River, Tijuca Forest, Rio de Janeiro, Brazil: Figs 1, 2, first stretch located at 380 meters of altitude; and Fig. 3, second stretch located at 420 meters of altitude.
Figure 1 in Seasonality and bait type driving the diversity of dung beetle (Scarabaeidae: Scarabaeinae) communities in urban remnants of the Atlantic Forest
Figure 1. Partial map of the state of Pernambuco, with emphasis on the remnants of the Atlantic Forest (Green) and the urban area (Pink) located on the outskirts of FURB Jaguarana in the municipality of Paulista and APA Aldeia-Beberibe in the municipality of Camaragibe, PE, Brazil.
Figure 3 in Seasonality and bait type driving the diversity of dung beetle (Scarabaeidae: Scarabaeinae) communities in urban remnants of the Atlantic Forest
Figure 3. Canonical Correspondence Analysis (CCA) with group formations related to separation and types of baits used in the collection of dung beetles at FURB Jaguarana (A) and APA Aldeia-Beberibe (B).
Figure 2 in Seasonality and bait type driving the diversity of dung beetle (Scarabaeidae: Scarabaeinae) communities in urban remnants of the Atlantic Forest
Figure 2. Differences between diversity index values (q0, q1, q2) for different types of baits (feces, carrion, millipedes) in the rainy and dry season at FURB Jaguarana (A) and APA Aldeia-Beberibe (B). Meaningfulness: <0.001'***'; <0.01'**'; <0.05'*'.
Fig. 2 in The role of fruit bats in plant community changes in an urban forest in Indonesia
Fig. 2. Total number of fruit bats captured in this study from the UI urban forest. Species are abbreviated as follows: Cbr = C. brachyotis; Cho = C. horsfieldii; Cmi = C. minutus; Csp = C. sphinx; Cti = C. titthaecheilus; Mmi = M. minimus; Mso = M. sobrinus; Ram = R. amplexicaudatus.
Fig. S1 in The role of fruit bats in plant community changes in an urban forest in Indonesia
Fig. S1. Weak correlation between forearm length of fruit bats and the diameter of fruits consumed (Spearman's correlation test, r = 0.15, df = 175, p <0.05).
Fig. 3 in The role of fruit bats in plant community changes in an urban forest in Indonesia
Fig. 3. Association results from vcd between bats and plants. Strength of bat-plant associations are indicated by the height and colour of the bars (Zeileis et al. 2007). The thickness of each bar suggested the number of fruit bats used certain plant species. The length of the bar showed the general diet breath of each fruit bat species. Each of the plant species is represented by a number (1=Filicium decipiens, 2=Nephelium lappaceum, 3=Syzygium sp., 4=Morinda citrifolia, 5=Musa paradisiaca, 6=Pometia pinnata, 7=Cecropia sp., 8=Calliandra sp., 9=Muntingia calabura, 10=Ficus benjamina, 11=Mimusops elengi, 12=Ficus septica, 13=Roystonia regia,14= Acacia mangium,15=Microcos tomentosa, 16=Antidesma sp., 17=Gmelina arborea, 18=Ficus callosa, 19=Syzygium polyanthum, 20=Macaranga sp., 21=Swietenia mahagoni, 22=Ficus hispida, 23= F. racemosa, 24= F. excelsa, 25= F. binnendijkii, 26=Dyospiros sp.). Each of it has a single bar, which depicts the association strength with each of the bat species. The bar graph with darker blue and wider indicates strong association.
Fig. 1 in The role of fruit bats in plant community changes in an urban forest in Indonesia
Fig. 1. Location of the Universitas Indonesia urban forest in South Jakarta, which extends into Depok, Indonesia. Fruit bats connect plant population among green areas in Jakarta and West Java. a) Serengseng Forest; b) Ragunan Zoo Forest; c) Bogor Botanical Garden.
Dataset for the paper "Data for Distribution of Vascular Plants (Tracheophytes) of urban forests and floodplains in the Tyumen city (Western Siberia)"
<p>Dataset associated with the manuscript “Data for Distribution of Vascular Plants (Tracheophytes) of urban forests and floodplains in the Tyumen city (Western Siberia)” submitted to the journal Data.</p>
Supplementary Material - Marine animal forests in turbid environments are overlooked seascapes in urban areas
<p>Figures S1, S2, and S3 of the manuscript "Marine animal forests in turbid environments are overlooked seascapes in urban areas" accepted in the open-access journal Ocean and Coastal Research (Soares et al. 2023)</p>
Data from: The city and forest bird flock together in a common garden: Genetic and environmental effects drive urban phenotypic divergence
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Genomic footprints of (pre) colonialism: Population declines in urban and forest túngara frogs coincident with historical human activity
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Data from: Urbanization strengthens vertical stratification of ant nutrient preferences in a temperate forest ecosystem
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Urban sensory conditions alter rival interactions and mate choice in urban and forest túngara frogs
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White oak and red maple foliar chemistry of urban and reference forests of the eastern US
Foliar chemistry values were obtained from two important native tree species (white oak (Quercus alba L.) and red maple (Acer rubrum L.)) across urban and reference forest sites of three major cities in the eastern United States during summer 2015 (New York, NY (NYC); Philadelphia, PA; and Baltimore, MD). Trees were selected from secondary growth oak-hickory forests found in New York, NY; Philadelphia, PA; and Baltimore, MD, as well as at reference forest sites outside each metropolitan area. In all three metropolitan areas, urban forest patches and references forest sites were selected based on the presence of red maple and white oak canopy dominant trees in patches of at least 1.5 hectares with slopes less than 25%, and well-drained soils of similar soil series within each metropolitan area. Within each city, several forest patches were selected to capture the variation in forest patch site conditions across an individual city. All reference sites were located in protected areas outside of the city and within intermix wildland-urban interface landscapes, in order to target similar contexts of surrounding land use and population density (Martinuzzi et al. 2015). Several reference sites were selected for each city, located within the same protected area considered representative of rural forests of the region. White oaks were at least 38.1 cm diameter at breast height (DBH), red maples were at least 25.4 cm DBH, and all trees were dominant or co-dominant canopy trees. The trees had no major trunk cavities and had crown vigor scores of 1 or 2 (less than 25% overall canopy damage; Pontius & Hallett 2014). From early July to early August 2015, sun leaves were collected from the periphery of the crown of each tree with either a shotgun or slingshot for subsequent analysis to determine differences in foliar chemistry across cities and urban vs. reference forest site types. The data were used to invstigate whether differences in native tree physiology occur between urban
Figure 4 in Notes on the bionomy of two spider wasp species in an urban forest fragment in Brazil
Figure 4. Nest of Auplopus cf. brasiliensis. The third cell broke during handling. Note the arrangement of the cells forming a cluster, the papillated surface suggesting the employment of several mud pellets to construct the cells. Scale bar = 0.5 cm.
Figure 1 in Notes on the bionomy of two spider wasp species in an urban forest fragment in Brazil
Figure 1. (A) Female of Auplopus cf. rufipes. Scale bar = 1 mm. (B) Male of Auplopus cf. brasiliensis. Scale bar = 3 mm.
Figure 3 in Notes on the bionomy of two spider wasp species in an urban forest fragment in Brazil
Figure 3. Development stages of Auplopus cf. rufipes. (A) Larva almost entirely developed feeding on a spider. Scale bar = 0.5 cm. (B) Larva probably in its third instar feeding. Scale bar = 0.5 cm. (C) Second instar larva. Scale bar = 0.5 cm. (D) Prey tightly trapped in the brood cell and egg placed on its opistosoma. Scale bar = 0.5 cm. (E) Egg in detail. Scale bar = 0.1 cm. (F) Last cell built with the prey and the egg placed on it. Scale bar = 0.5 cm.
Figure 2 in Notes on the bionomy of two spider wasp species in an urban forest fragment in Brazil
Figure 2. Nest of Auplopus cf. rufipes. (A) Arrangement of cells inside the trap nest. Scale bar = 1 cm. (B) Nest in profile showing an overlay on the first cell and the cells leaning. Scale bar = 1 cm. (C) Cell lip-shaped structure before provision. Scale bar = 0.5 cm. (D) Brood cells glued together, one of them with an emergence hole. Scale bar = 0.5 cm.
ScienceDex guides
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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
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.