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Movement Metrics for Common Snook and Atlantic Tarpon in the Coastal Everglades, Florida, USA, July 2016 to April 2021
This dataset contains acoustic telemetry derived residency and movement metrics for Common Snook (Centropomus undecimalis) and Atlantic Tarpon (Megalops atlanticus) tracked in two neighboring estuarine systems in the coastal Florida Everglades by the Coastal Everglades Lakes Acoustic Array. Data were summarized at the quarter-season level (early dry, late dry, early wet, late wet) across multiple years (2016–2021), resulting in 326 records and 15 variables. Each record includes metadata on species identity, year, system, and season, as well as individual-level residency time statistics (minimum, maximum, mean, variance), number of lakes visited, and proportional system use. The dataset provides a standardized summary of spatial and temporal variation in Snook and Tarpon habitat use, suitable for investigating seasonal residency and patterns of movement behavior. Data collection for this package is complete.
Soil movement across black grama and mesquite ecotone transects in the Jornada Basin, southern New Mexico, USA, 1933-2011
This package contains data from a study that measured long-term soil movement in areas undergoing mesquite invasion on the Jornada Experimental Range from 1933-2011. Data consist of height measurements of soil on two long-term transects established in the Natural Revegetation Exclosure (NatReveg) in 1933 and an exclosure in Pasture 8b in 1935. In 1933, about half of the NatReveg exclosure was covered with mesquite dunes. Grasses dominated the non-dune portion, but mesquite plants were present. Approximately one-third of the NatReveg site exclosure was sprayed with 2,4,5-T herbicide for mesquite control in 1966-68. Additional herbicide treatments were conducted upon the sprayed portion in 1969-72. The 1731-m NatReveg exclosure transect runs north-south through the center of the exclosure and extends 61 m (200ft) beyond the boundary fence on either end. The 457-m Pasture 8b transect is oriented WSW-ENE and was established in an area where mesquite dunes were large and well established. The predominant soils in this exclosure are deep loamy sands. Soil movement was measured by the distance between the soil surface and a notch in 50 cm T-posts located every 15.2 m (50 ft). Transects were measured in 1950 (8b only), 1955 (8b only), every five years from 1980-2000, and most recently in 2011. Most steel posts were re-measured at these intervals, but some were lost due to excavation or burial. These were replaced with a new baseline notch height initiated on the posts. Data correspond to each year of collection, as well as measures (in cm) of soil deposition or deflation during the intervals. This study is complete. For further information, see: Gibbens, R.P., J.M. Tromble, J.T. Hennessy, and M. Cardenas, 1983. "Soil movement in mesquite dunelands and former grasslands of southern New Mexico from 1933 to 1980." Journal of Range Management 36:145-148.
Data for paper titled : Comparing Clothing-Mounted Sensors with Wearable Sensors for Movement Analysis and Activity Classification (published in Sensors (MDPI))
<p>Data for paper titled : Comparing Clothing-Mounted Sensors with Wearable Sensors for Movement Analysis and Activity Classification (published in Sensors (MDPI))</p>
Fig. 2 in Movement and longitudinal distribution of a migratory fish (Salminus brasiliensis) in a small reservoir in southern Brazil
Fig. 2. Total time spent by dourados (Salminus brasiliensis) in the reservoir (Tin), total time spent in an unknown location (Tun) and total time spent outside of the reservoir in a stretch of the upstream Erechim river (Tout). ANOVA with permutation tested for differences among groups (F(2,54) = 87.17; p <0.0002). The numbers above the plots represent the number of individuals. Different letters above the plots represent significant differences according to Tukey's test. Circles represent outlier values; the heavy horizontal line crossing the box is the median; the bottom and top of the box are the lower and upper quartiles, respectively; and the whiskers are the minimum and maximum values.
Fig. 5 in Fish movement in an Atlantic Forest stream
Fig. 5. Relationship between distance (m) moved by fishes and seasons (dry and rainy) of all moving species from Ubatiba stream, Southeast, Brazil.
Fig. 2 in Fish movement in an Atlantic Forest stream
Fig. 2. Schematic representation of the study area. Numbers were designated according to the distance of each stretch to the first stretch (0 m). Arrows indicate the water flow.
Fig. 1. Ubatiba stream system showing all the four sampling sites. P1 in Fish movement in an Atlantic Forest stream
Fig. 1. Ubatiba stream system showing all the four sampling sites. P1 is the most upstream site and P4 is the most downstream site.
Standstill to the beat: Differences in involuntary movement responses to simple and complex rhythms (SOUND STIMULI)
<p>Sound stimuli used in the 2019 "Nordic Championship of Standstill" experiment, presented in the paper titled "Standstill to the beat: Differences in involuntary movement responses to simple and complex rhythms".</p>
Figure 11 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 11. Relationships of human presence, horse key summer range (KSR) use, and lion numbers in the Montgomery Pass Wild Horse Territory (MPWHT). Human presence (May– September) is presented as per cent of its highest year. Horse KSR use is presented as per cent of the total population using the KSR. Adult lion numbers are presented as the percentage of the maximum single-year lion number.
Figure 6 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 6. Montgomery Pass Wild Horse Territory (MPWHT) horse use of non-key summer range (KSR) areas. Use outside the MPWHT primarily includes areas east of Basalt and west of Adobe Valley.
Figure 5. Changes from 1987 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 5. Changes from 1987 to 2007 in patterns of the geographic distribution of wild horses in the Montgomery Pass Wild Horse Territory (MPWHT). The central, lightly shaded area is the key summer range (KSR). The black mark within it is the highest elevation in the Territory (elevation decreases 360 degrees around it throughout). Dark shaded areas indicate regular horse use and represent> 90% of the population. Many wild horse populations in the intermountain west accommodate to seasonal conditions, spending winter at lower elevations and summer at higher elevations. The pattern across years in the MPWHT changed from summer horse concentration in the KSR to decreasing return to KSR from winter range. In addition to establishment of decreased KSR use and increased year-round use of historical winter-range areas, expansion of the geographic use areas occurred in the latter, including seasonal use beyond MPWHT map boundaries.
Figure 8 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 8. The relationship of key summer range (KSR) horse use and carrying capacity in the context of the Montgomery Pass Wild Horse Territory (MPWHT) horse population. As KSR horse numbers decreased, use outside the KSR increased. Total population range use is presented as a percentage of KSR carrying capacity. As total population increased across years, it remained <80% of carrying capacity for KSR alone, suggesting that considerable population growth can continue without reaching carrying capacity.
Figure 4 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 4. Relationship of mountain lions and foal survival in the Montgomery Pass Wild Horse Territory (MPWHT). Data are based on annual assessment between May and September. The majority of predation occurred in the key summer range (KSR). Adult lion numbers and foal survival in the MPWHT: foal survival is presented as the ratio of currentyear yearlings to previous-year foals expressed as a percentage, lion numbers are for individual lions documented by telemetry, track and/or sighting. The majority of lions were recorded in the KSR.
Figure 3 in Environmental influences on movements and distribution of a wild horse (Equus caballus) population in western Nevada, USA: a 25-year study
Figure 3. Annual total number of horses in the Montgomery Pass wild horse population. Numbers represent reliable estimate for all range areas (not complete enumeration).
Figure 50. Pegomya solennis, mandibles removed from a in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figure 50. Pegomya solennis, mandibles removed from a puparium, ventral view, maximum length 0.1 mm.
Figure 53 in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figure 53. Stegana coleoptrata, thorax and head cleared in KOH, lateral view, head to the right, as = anterior spiracle; ms = mesothorax; mt = metathorax; os = oral sclerite; pro = prothorax; ps = pseudocephalon.
Figures 31 in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figures 31. Neophyllomyza acyglossa. (A) Preserved larva, anterior end, lateral view, length 4.5 mm. Lunging, stills from Film 14: (B) limit of forward extension; (C) bending of the intermediate sclerite; (D) limit of bending in the intermediate sclerite.
Figure 26 in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figure 26. Calliphora vomitoria, pseudocephalon with mandibles and cutting plates depressed, still from a film, apical view.
Figures 43 in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figures 43. Pegomya solennis, larva feeding in a leaf mine on Rumex acetosa (Polygonaceae), stills from Film 18. (A) Position at the start of a feeding lunge; (B) position at the end of a feeding lunge.
Figures 38 in Diverse mechanisms of feeding and movement in Cyclorrhaphan larvae (Diptera)
Figures 38. Tephritis vespertina. (A) Feeding damage caused by the third stage larva inside the flowerhead of Hypochoeris radicata L. (Asteraceae); (B) larva in situ.
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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.