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212 results for “Land use change”

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zenodo40/100

Land use and land cover changes in the contiguous United States from 1630 to 2020

<p>Through integrating multi-source data including high-resolution remote sensing image-based land use and land cover (LULC) data, model-based land use products, and historical land archives, we reconstructed historical LULC at an annual time scale and 1 km x 1 km resolution in the contiguous United States (CONUS) from 1630 to 2020. Compared to other historical LULC datasets, our data can capture the major characters of LULC as well as provide more accurate information with higher spatial and temporal resolution. The LULC data can be used for regional studies in a wide range of topics including LULC impacts on the ecosystem, biodiversity, water resource, carbon and nitrogen cycles, and greenhouse gas emissions.</p>

opencc-by-4.0Mar 2022View details →
zenodo40/100

Supporting data: Land-use change alters the mechanisms assembling rainforest mammal communities in Borneo

<p>These supporting data files were&nbsp;used in the analyses for a forthcoming<em>&nbsp;</em>paper (DOI to be confirmed). The two files consist of:&nbsp;</p> <p>1. Combined camera trap and live trap species-abundance matrix. Each row corresponds to a separate&nbsp;location, with species in different columns. Old-growth forest, logged forest and oil palm plantation locations have the prefixes &quot;Old&quot;, &quot;Log&quot; and &quot;Palm&quot;, respectively. Values in each cell are the number of independent captures (as defined in the paper) per seven&nbsp;days summed over the camera- and live-trapping protocols.</p> <p>2. Covariate data for each location, covering habitat structure, topography and local landscape context (covariates as defined in the paper).&nbsp;</p>

opencc-by-nc-4.0Aug 2017View details →
dryad40/100

Differential impacts of land use change on multiple components of common Milkweed (Asclepias syriaca) pollination success

<p>Land-use change is one the greatest threats to biodiversity and is projected to increase in magnitude in the coming years, stressing the importance of better understanding how land-use change may affect vital ecosystem services, such as pollination. Past studies on the impact of land-use change have largely focused on only one aspect of the pollination process (e.g. pollinator composition, pollinator visitation, pollen transfer), potentially misrepresenting the full complexity of land-use effects on pollination services. Evaluating the impacts across multiple components of the pollination process can also help pinpoint the underlying mechanisms driving land-use change effects. This study evaluates how land-use change affects multiple aspects of the pollination process in common milkweed populations, including pollinator community composition, pollinator visitation rate, pollen removal, and pollen deposition. Overall, land-use change altered floral visitor composition, with small bees having a larger presence in developed areas. Insect visitation rate and pollen removal were also higher in more developed areas, perhaps suggesting a positive impact of land-use change. However, pollen deposition did not differ between developed and undeveloped sites. Our findings highlight the complexity evaluating land-use change effects on pollination, as these likely depend on the specific aspect of pollination evaluated and on the of the intensity of disturbance. Our study stresses the importance of evaluating multiple components of the pollination process in order to fully understand overall effects and mechanisms underlying land-use change effects on this vital ecosystem service.</p>

opencc-zeroMay 2024View details →
zenodo40/100

Figure 1 in Impact of Drought and Land - Use Changes on Surface - Water Quality and Quantity: The Sahelian Paradox

Figure 1. - Location of the sampling site (star) of flying gurnard Dactylopterus volitans in the Eastern English Channel.

opencc-by-4.0Dec 2013View details →
zenodo40/100

Figure 3 in Impact of Drought and Land - Use Changes on Surface - Water Quality and Quantity: The Sahelian Paradox

Figure 3. - Specimen of flying gurnard Dactylopterus volitans (MNHN 2013-0612; 47 cm TL) caught in the Eastern English Channel in 2011.

opencc-by-4.0Dec 2013View details →
zenodo40/100

Figure 2 in Impact of Drought and Land - Use Changes on Surface - Water Quality and Quantity: The Sahelian Paradox

Figure 2. - Whole otolith of flying gurnard (Dactylopterus volitans) with annotation of growth rings (red stars).

opencc-by-4.0Dec 2013View details →
zenodo40/100

Figure S4 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S4. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating annual forb plant functional types (PFTs).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure S5 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S5. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating perennial forb plant functional types (PFTs).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure S3 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S3. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating perennial grass plant functional types (PFTs).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure S1 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S1. Principal Co-ordinate Analysis (PCoA) scatter diagram of the species-trait matrix revealing a strong clustering based on life history.

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure 3 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure 3. Herbaceous species (left) and trait (right) diversity measures benchmarked against the mean value calculated for the untransformed (protected) area (----) across transformed land-use types. Vertical bars denote 0.95 confidence intervals. Significant deviations from the protected area (Sidak posthoc pairwise comparison; p&lt;0.05) are denoted by (*).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure S2 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S2. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating annual grass plant functional types (PFTs).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure 4 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure 4. Principal Component Analysis (PCA) ordination of land-use type sampling plots correlated with plant functional types (PFT's). CAF (Communal abandoned fields); CR (Communal rangelands); NRSM (Naturally restored strip mine); RASM (Recently active strip mine); UMV (Untransformed Mopaneveld).

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure 2 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure 2. Multidimensional Scaling (NMDS) ordination of sampling plots representing herbaceous species assemblages across land-use types. Broad groupings are encircled.

opencc-by-4.0Feb 2021View details →
zenodo40/100

Figure 1 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure 1. Study area and locality of sampled sites. Strip mines and untransformed Mopaneveld is located at Pompeye (top) and communal areas at Lulekani (bottom).

opencc-by-4.0Feb 2021View details →
zenodo40/100

FIGURE 4 in Land-use changes affect the functional structure of stream fish assemblages in the Brazilian Savanna

FIGURE 4 | Structural equation model diagrams showing the effects of landscape degradation (CDI) on the functional structure of stream fish assemblages from the Araguari River basin. CDI influenced functional diversity mediated by alterations in habitat heterogeneity and stability (A. Model fit: X2 = 32.8, df = 25, p = 0.51). CDI also influenced functional identity, mediated by changes in habitat type (B. Model fit: X2 = 44.9, df = 18, p = 0.13). Arrows indicate positive (black) and negative (gray) significant direct effects (p &lt;0.05; *p &lt;0.10), with thickness proportional to their power (standardized path coefficients along arrows). Biodiversity metrics – FRic: Functional Richness; FDiv: Functional Divergence; FEve: Functional Evennes; FSpe: Functional Specialization; FOri: Functional Originality; CWM1-3: Functional Identity. For physical-habitat codes, calculation and ecological meaning, see Tab. 1.

opencc-by-4.0Oct 2021View details →
zenodo40/100

FIGURE 5 in Land-use changes affect the functional structure of stream fish assemblages in the Brazilian Savanna

FIGURE 5 | Ecomorphological space showing the position of each fish species (36) from the Araguari River basin. Each plot represents two axes of a principal component analysis (PCA), where species are plotted according to their respective trait values. Codes at the ends of the arrows are the most important ecomorphological traits for each PCA axis. For trait and species codes, see Tab. 2 and Tab. S3, respectively).

opencc-by-4.0Oct 2021View details →
zenodo40/100

FIGURE 2 in Land-use changes affect the functional structure of stream fish assemblages in the Brazilian Savanna

FIGURE 2 | Examples of landscape and local-habitat conditions of the streams sampled across a degradation gradient in the Cerrado: A. Streams with a small strip of riparian forests in landscapes dominated by mechanized agriculture; B. Stream with relatively well-preserved local conditions, including forest on both banks; C. Stream surrounded by intermediate riparian cover; and D. Stream running in pasture areas without any forest.

opencc-by-4.0Oct 2021View details →
zenodo40/100

FIGURE 3 in Land-use changes affect the functional structure of stream fish assemblages in the Brazilian Savanna

FIGURE 3 | Predictions tested using structural equation modeling, indicating the expected pathways (arrows) for the effects of catchment degradation (CDI) on stream physical habitat and, consequently, on the functional structure of the fish assemblages. Land use is expected to influence the functional diversity mediated by alterations in habitat heterogeneity and stability (A), and to influence functional identity, mediated by changes in habitat type (B). Arrows indicate expected effects between predictive and response variables, which can be positive (black continuous line), negative (gray continuous line) or non-directional (dashed lines). For physical-habitat codes, calculation and ecological meaning, see Tab. 1.

opencc-by-4.0Oct 2021View details →
zenodo40/100

FIGURE 1 in Land-use changes affect the functional structure of stream fish assemblages in the Brazilian Savanna

FIGURE 1 | Headwater streams (N = 40; black dots) sampled for fish and local physical habitat. All sites drain to Nova Ponte Reservoir in the Araguari River basin, Upper Paraná River, Minas Gerais, Brazil.

opencc-by-4.0Oct 2021View details →

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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.

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OpenNeuro

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Last verified 2026-04-29Open record