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136 results for “rangeland”

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dryad32/100

Data from: Characterization of puma-livestock conflicts in rangelands of central Argentina

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publicNov 2017View details →
dryad32/100

Data from: Leaf carbon and oxygen isotopes are coordinated with the leaf economics spectrum in Mediterranean rangeland species

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publicNov 2018View details →
dryad32/100

Data from: A burning issue: Savanna fire management can generate enough carbon revenue to help restore Africa’s rangelands and fill protected area funding gaps

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publicNov 2021View details →
dryad32/100

Data from: Patterns of rangeland productivity and land ownership: implications for conservation and management

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publicJan 2019View details →
dryad32/100

Data from: Habitat associations of bats in a working rangeland landscape

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publicDec 2018View details →
dryad32/100

Rainfall pulses mediate long-term plant community compositional dynamics in a semi-arid rangeland

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publicSep 2020View details →
dryad32/100

Data from: Plant species richness and shrub cover attenuate drought effects on ecosystem functioning across Patagonian rangelands

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publicSep 2014View details →
dryad32/100

Morphoecological characteristics of grasses used to restore degraded semi-arid African rangelands

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publicNov 2020View details →
dryad32/100

Data from: Ungulate distributions in a rangeland with competitors, predators, and pastoralists

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publicJan 2017View details →
zenodo28/100

Carbon stocks from rangeland riparian restoration, northern California

<p>Data on carbon accumulation in soils and woody biomass as a result of rangeland riparian restoration in northern California. These data accompany a paper expected to&nbsp;appear in Carbon Balance and Management.</p>

opencc-by-4.0Dec 2019View details →
dryad28/100

Identifying relationships between multi-scale social-ecological factors to explore ungulate health in a Western Kazakhstan rangeland

<p>1. Rangelands are multi-use landscapes which are socially and ecologically important in different ways. Among other interactions, shared use of rangelands by wildlife and livestock can lead to disease transmission. Understanding wildlife and livestock health and managing disease transmission in rangelands requires an integration of social and ecological knowledge.</p> <p>2. Using the example of Western Kazakhstan, home to two types of ungulate hosts, the critically-endangered saiga antelopes, <i>Saiga tatarica</i>, and livestock, we conducted a cross-scale analysis of social-economic, ecological and climatic factors that contribute to transmission of diseases. We focused on Gastro-intestinal Nematodes (GINs) because they are transmitted between hosts that share pasture and they affect ungulate fitness. We used an interdisciplinary social-ecological methods approach which included conducting fecal egg counts of GINs in saigas and livestock, semi-structured interviews and focus group discussions with livestock owners and herders in the region, and triangulation of information through secondary sources.</p> <p>3. Livestock rearing was done in two ways a) village-based livestock and b) outlying farms. The latter overlapped more with saigas. Village-based livestock had significantly higher worm burdens than those on outlying farms, which had comparable burdens to saigas. Various factors exacerbate GIN prevalence and transmission: Veterinary services are minimal; both saiga and livestock numbers are increasing; and changing climate is increasing farmers' dependence on shared pastures for hay production. It will be crucial for saiga conservationists to engage in multi-pronged conservation interventions, which are evaluated and adapted through the lens of rural livelihoods and the livestock health on which they depend.</p> <p>4. <em>Synthesis and Application: </em>Our work provides researchers and practitioners with an avenue to better understand complex inter-relationships and plan interventions within rangelands, while viewing host health from an interdisciplinary perspective - ultimately working towards wildlife conservation whilst safeguarding livelihoods across the world's rangelands.</p>

opencc-zeroNov 2021View details →
zenodo28/100

Figure 3 from: Zembrzuski D, Woller DA, Jech L, Black LR, Reuter KC, Overson R, Cease A (2021) Establishing the nutritional landscape and macronutrient preferences of a major United States rangeland pest, Melanoplus sanguinipes, in field and lab populations. Journal of Orthoptera Research 30(2): 163-172. https://doi.org/10.3897/jor.30.61605

Figure 3 Performance experiments. Survival and specific growth rates of grasshoppers from the long-term lab colony no-choice diet experiments. A. The specific growth rates for each diet treatment. Diamonds indicate the mean and bolded lines indicate the median. Boxes are +/- 25%, lines represent minimum and maximum values excluding extreme values, and dots indicate data points &gt; 1.5 farther from the box edge than the interquartile range. Lower case letters indicate differences from Mann-Whitney post-hoc analyses. B. The proportion of grasshoppers surviving through time on each diet treatment. Most diet treatments did not have individuals die until the 5th day of the experiment, and most treatments except 7p:35c had minimal deaths (although there were no significant differences among treatments). C. Proportion of grasshoppers molting to adults over time. Most of the diets saw increases in molting from days 5–7, except diet treatment 7p:35c, which was delayed and had the least number of grasshoppers successfully molt (significantly different from all other treatments).

opencc-by-4.0Dec 2021View details →
zenodo28/100

Figure 2 from: Zembrzuski D, Woller DA, Jech L, Black LR, Reuter KC, Overson R, Cease A (2021) Establishing the nutritional landscape and macronutrient preferences of a major United States rangeland pest, Melanoplus sanguinipes, in field and lab populations. Journal of Orthoptera Research 30(2): 163-172. https://doi.org/10.3897/jor.30.61605

Figure 2 Field IT compared to nutritional landscape. A, B. Grasshopper intake targets of the field populations (black solid line) alongside the nutrient contents of grasses (triangles) and forbs (circles) collected from the same fields. The grey solid line represents the intake target from the other field population. The dotted line represents a 1p:1c ratio. C, D. The average Euclidean distance between the plants (triangles and circles in A and B) and either the grasshopper IT from each location or the 1p:1c line. * denotes a significant difference between the Euclidean distances calculated from the IT and the 1p:1c line.

opencc-by-4.0Dec 2021View details →
zenodo28/100

Figure 1 from: Zembrzuski D, Woller DA, Jech L, Black LR, Reuter KC, Overson R, Cease A (2021) Establishing the nutritional landscape and macronutrient preferences of a major United States rangeland pest, Melanoplus sanguinipes, in field and lab populations. Journal of Orthoptera Research 30(2): 163-172. https://doi.org/10.3897/jor.30.61605

Figure 1 Field populations and lab population ITs. Average intake target (+/- SEM) for two field populations, Bliss and Boise, ID, and the lab colony. The dashed line represents a 1:1 ratio of protein and carbohydrates, and the crosses on the data points represent SE.

opencc-by-4.0Dec 2021View details →
zenodo28/100

Figure 1 from: Branson DH (2017) Grasshopper species composition shifts following a severe rangeland grasshopper outbreak. Journal of Orthoptera Research 26: 7-10. https://doi.org/10.3897/jor.26.14542

Figure 1 - Proportional composition for each of the three major grasshopper species averaged across random catches in a given year from 1999 to 2003.

opencc-by-4.0Jun 2017View details →
zenodo28/100

Figure 1 from: Branson DH (2017) Grasshopper species composition shifts following a severe rangeland grasshopper outbreak. Journal of Orthoptera Research 26: 7-10. https://doi.org/10.3897/jor.26.14542

Figure 1 - Proportional composition for each of the three major grasshopper species averaged across random catches in a given year from 1999 to 2003.

opencc-by-4.0Jun 2017View details →
zenodo28/100

Supplementary material 7 from: Lee T, Alemseged Y, Mitchell A (2018) Dropping Hints: Estimating the diets of livestock in rangelands using DNA metabarcoding of faeces. Metabarcoding and Metagenomics 2: e22467. https://doi.org/10.3897/mbmg.2.22467

Taxon accumulation curves for Dorper specimens.

opencc-zeroApr 2018View details →
zenodo28/100

Supplementary material 14 from: Lee T, Alemseged Y, Mitchell A (2018) Dropping Hints: Estimating the diets of livestock in rangelands using DNA metabarcoding of faeces. Metabarcoding and Metagenomics 2: e22467. https://doi.org/10.3897/mbmg.2.22467

Family level taxa (BOLD Data), at 3 minimum read depth.

opencc-zeroApr 2018View details →
zenodo28/100

Supplementary material 3 from: Lee T, Alemseged Y, Mitchell A (2018) Dropping Hints: Estimating the diets of livestock in rangelands using DNA metabarcoding of faeces. Metabarcoding and Metagenomics 2: e22467. https://doi.org/10.3897/mbmg.2.22467

DNA barcode results (GenBank) for plant reference samples.

opencc-zeroApr 2018View details →
zenodo28/100

Supplementary material 12 from: Lee T, Alemseged Y, Mitchell A (2018) Dropping Hints: Estimating the diets of livestock in rangelands using DNA metabarcoding of faeces. Metabarcoding and Metagenomics 2: e22467. https://doi.org/10.3897/mbmg.2.22467

Family level taxa (GenBank data), at 3 minimum read depth.

opencc-zeroApr 2018View details →

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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

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