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171 results for “home range”

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zenodo32/100

Lophuromys medicaudatus, L. woosnami, and L. luteogaster are in subgenus Kivumys and woosnami species group. Monotypic. Distribution. Endemic to the Albertine Rift, occurring around Lake Kivu in E DR Congo and Rwanda and SW Uganda (Bwindi). Descriptive notes. Head—body 92-112 mm, tail 73-95 mm, ear 15-19 mm, hindfoot 18-23 mm; weight 29-43 g. Similar to other species in subgenus Kivumys, the Western Rift Brush-furred Rat has unspeckled pelage, and tail ¢.85% of head-body length. Dorsum is uniform dark brown-olive, and venter is orange. Females have three pairs of mammae. Habitat. Mountain swamps and mountain forests at elevations of 1850-2500 m. Food and Feeding. The Western Rift Brush-furred Rat is omnivorous; diets contain 30-100% arthropods, mollusks, seeds, and fruits. Breeding. Female Western Rift Brush-furred Rats can have 1-2 embryos. Pregnant females were observed in February, April, and July. Activity patterns. The Western Rift Brush-furred Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Vulnerable on The IUCN Red List. The Western Rift Brush-furred Rat has never been found in modified secondary environment and is quite rare. Bibliography. Dieterlen (1976b, 1987 2013g), Kasangaki et al. (2003), Verheyen et al. (1996). in Muridae

Lophuromys medicaudatus, L. woosnami, and L. luteogaster are in subgenus Kivumys and woosnami species group. Monotypic. Distribution. Endemic to the Albertine Rift, occurring around Lake Kivu in E DR Congo and Rwanda and SW Uganda (Bwindi). Descriptive notes. Head—body 92-112 mm, tail 73-95 mm, ear 15-19 mm, hindfoot 18-23 mm; weight 29-43 g. Similar to other species in subgenus Kivumys, the Western Rift Brush-furred Rat has unspeckled pelage, and tail ¢.85% of head-body length. Dorsum is uniform dark brown-olive, and venter is orange. Females have three pairs of mammae. Habitat. Mountain swamps and mountain forests at elevations of 1850-2500 m. Food and Feeding. The Western Rift Brush-furred Rat is omnivorous; diets contain 30-100% arthropods, mollusks, seeds, and fruits. Breeding. Female Western Rift Brush-furred Rats can have 1-2 embryos. Pregnant females were observed in February, April, and July. Activity patterns. The Western Rift Brush-furred Rat is terrestrial. Movements, Home range and Social organization. No information. Status and Conservation. Classified as Vulnerable on The IUCN Red List. The Western Rift Brush-furred Rat has never been found in modified secondary environment and is quite rare. Bibliography. Dieterlen (1976b, 1987 2013g), Kasangaki et al. (2003), Verheyen et al. (1996).

opennotspecifiedNov 2017View details →
zenodo32/100

Figure 2 in Population densities and home range of the vulnerable Pyrenean brook newt in its core aquatic habitat

Figure 2. Number of captures of the Pyrenean brook newt estimated according to different metrics: mean temperature, mean flow and coefficient of variation of flow; calculated at different time steps: day of capture, last 72h and last month; for Fougax and Salau.The black line indicates the mean of the effects and the grey area indicates the 95% confidence interval.

opennotspecifiedFeb 2022View details →
zenodo32/100

Figure 1 in Population densities and home range of the vulnerable Pyrenean brook newt in its core aquatic habitat

Figure 1. Location of the three Pyrenean brook newt populations in the Ariège and Aude departments (France). Data source: elevation (ALTI © DB 25 m, IGN), hydrographic network (CARTHAGE © DB, Sandre).

opennotspecifiedFeb 2022View details →
zenodo32/100

Figure 3 in Home range behaviour in male and female poison frogs in Amazonian Peru (Dendrobatidae: Ranitomeya reticulata)

Figure 3. Box plots illustrating the average distance of male and female individuals of Ranitomeya reticulata to the nearest ground bromeliad.

opennotspecifiedDec 2010View details →
zenodo32/100

Figure 2 in Home range behaviour in male and female poison frogs in Amazonian Peru (Dendrobatidae: Ranitomeya reticulata)

Figure 2. (A) The overlapping k95 home range and k50 core areas of two neighbouring males (top) and comparison of the two different home range estimation methods (bottom). The outer solid lines represent the k95 kernel area, the dashed line encloses the Minimum Convex Polygon area and the inner spotted circles represent the k50 core areas, while the positions of the observation of the individuals are indicated by the grey points. The filled light grey region shows the overlapping part of the home range areas whereas there is no overlap of the core areas of the two specimens. (B) Example of the k95 home range and k50 core areas of two males (m; black lines) and two females (f; grey lines) and the positions of ground bromeliads (black stars) inside plot 2.

opennotspecifiedDec 2010View details →
zenodo32/100

Figure 1 in Home range behaviour in male and female poison frogs in Amazonian Peru (Dendrobatidae: Ranitomeya reticulata)

Figure 1. Box plots illustrating the home range extensions for male and female individuals of Ranitomeya reticulata using different estimation methods. In the upper right corner, the species with its almost unicoloured dorsal side (orange to red in life) is illustrated. [This figure can be viewed in colour online.]

opennotspecifiedDec 2010View details →
dryad32/100

Data for: Seasonal home range and habitat selection patterns of sika deer Cervus nippon in southern Hokkaido, Japan

<p>In 1980 and 1981, eight and nine individual sika deer <em>Cervus nippon</em> were reintroduced in southern Hokkaido, Japan, respectively, to address population declines in this species during 1900s. As recent population growth has led to human–wildlife conflicts, this study investigated the responses of sika deer to resource availability and geomorphic factors during the summer and winter seasons in southern Hokkaido. Global positioning system-collared data collected from 2016 to 2018 were used to assess the home range patterns and habitat selection of 14 female sika deer located in Mount Esan and Shiriuchi. The core home range size was defined using a 50% kernel density estimation that indicated a larger home range in winter than summer for all deer. Habitat selection was assessed using generalized linear mixed models. The results showed variation in habitat selection between resident deer of Mount Esan and Shiriuchi, as well as migratory deer in Shiriuchi during summer. Resident deer in Mount Esan and Shriuchi preferred areas closer to crops during summer. Interaction effects revealed that migratory deer utilized natural grassland close to forest edge habitat in Shiriuchi. By contrast, resident deer in Shiriuchi selected forest edge habitat and natural grasslands close to crops. In winter, low elevation was the most important habitat factor for all deer across the study area. Thus, sika deer habitat selection depends on resource availability in summer and topographic factors in the winter.</p>

opencc-zeroDec 2022View details →
zenodo32/100

Fig. 2 in Demographic and environmental correlates of home ranges and long-distance movements of Mohave ground squirrels

Fig. 2.—Back-transformed model fitted values from the best-performing model of size of annual home ranges (a) by sex (mean ± SE) and (b) the standard deviation (SD) of elevation for Mohave ground squirrels in the Freeman Gulch study area, Mojave Desert, California, 2003–2004. Gray bands in (b) represent 95% confidence intervals.

opennotspecifiedOct 2022View details →
zenodo32/100

Fig. 1 in Demographic and environmental correlates of home ranges and long-distance movements of Mohave ground squirrels

Fig. 1.—Map of the Freeman Gulch study area in the west-central portion of the geographic range of the Mohave ground squirrel (MGS) in the Mojave Desert, California. The study area is approximately indicated by a minimum convex polygon drawn around all MGS radiotelemetry locations collected in 2003–2004. The Coso Range, in which MGS studies were conducted in the 1990s, is located in the northern portion of the MGS range. The top inset map shows juvenile and adult MGS locations within the Freeman Gulch study area. The cluster of locations in the extreme northeast of the inset was from a single individual that made a long-distance movement as a juvenile in 2003 and established a home range as an adult the following year. The bottom inset map shows the location of the MGS range in southern California.

opennotspecifiedOct 2022View details →
zenodo32/100

FIG. 6. Standardized Precipitation Index for the 6 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 6. Standardized Precipitation Index for the 6-mo interval that encompasses winter rainfall at Palm Springs during the course of the study. Rainfall intervals were standardized against all other November through April intervals since 1927/28. An index of 0 to -0.99 indicates mild drought, -1.00 to -1.49 moderate drought, -1.50 to -1.99 severe drought, and -2.00 to -3.00 extreme drought. Positive index values indicate wet years and horizontal lines designate severe drought-year and severe wet-year thresholds.

opennotspecifiedApr 2020View details →
zenodo32/100

FIG. 5 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 5. Home range exhibits logistic growth over time for both sexes of Coachella Fringe-Toed Lizards (U. inornata). The asymptote estimated from a logistic growth equation is 1,025 m2 for females and 4,523 m2 for males.

opennotspecifiedApr 2020View details →
zenodo32/100

FIG. 2 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 2. Age-size relationship for the Coachella Fringe-Toed Lizard (Uma inornata) showing the mean length (SVL) at each age with sample sizes for all individuals measured during the study. Vertical bars are at 95% confidence interval (CI). Data include individuals that were measured multiple times during the study (n = 3,316).

opennotspecifiedApr 2020View details →
zenodo32/100

FIG. 1 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 1. The study site showing sparse vegetation and aeolian sand; lizards use the accretion dunes that form on the leeward side of vegetation. An adult female Coachella Fringe-Toed Lizard (Uma inornata) is shown in the inset.

opennotspecifiedApr 2020View details →
zenodo32/100

FIG. 3 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 3. Sighting frequency of all individual Coachella Fringe-Toed Lizards (Uma inornata) between 1985 and 2015.

opennotspecifiedApr 2020View details →
zenodo32/100

FIG. 4 in A Long-term Study of Home Range of Coachella Fringe-Toed Lizards, Uma inornata

FIG. 4. Example of changes in HR size and location over the lifetime of an individual male Coachella Fringe-Toed Lizard (U. inornata) from the 1995 hatchling cohort.

opennotspecifiedApr 2020View details →
dryad32/100

Data from: Ectothermy and the macroecology of home range scaling in snakes

Open the record for dataset details and reuse information.

publicDec 2020View details →
dryad32/100

Intrinsic traits, social context, local environment, and home range size and fidelity data from a field study of sleepy lizards, 2009 - 2017

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publicJan 2022View details →
dryad32/100

Data from: Season and site fidelity determine home range of dispersing and resident juvenile Greenland cod (Gadus ogac) in a Newfoundland fjord

Open the record for dataset details and reuse information.

publicFeb 2015View details →
dryad32/100

Data from: Scale-dependent home range optimality for a solitary omnivore

Open the record for dataset details and reuse information.

publicJan 2019View details →
dryad32/100

Data from: From fine-scale foraging to home ranges: a semi-variance approach to identifying movement modes across spatiotemporal scales

Open the record for dataset details and reuse information.

publicOct 2013View details →

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