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332 results for “environmental conditions”
Figure 8 in Investigation of roost composition of passerine birds in different environmental conditions
Figure 8. Roosts composition of birds recorded from the city road, Sheikhupura. S.E. = Standard Error.
Figure 3 in Investigation of roost composition of passerine birds in different environmental conditions
Figure 3. Roost composition of bird species from forest plantations, Gutwala wildlife sanctuary, Faisalabad. S.E. = Standard Error.
Fig. 2 in Environmental conditions predict helminth prevalence in red foxes in Western Australia
Fig. 2. Prevalence of Uncinaria stenocephala and Dipylidium caninum from red foxes at each sampling location.
Fig. 1 in Environmental conditions predict helminth prevalence in red foxes in Western Australia
Fig. 1. Prevalence of helminths in red foxes (n=147) from sampling locations throughout southwest Western Australia. Numbers in parentheses indicate sample size at each location.
Figure 2 in Onset and duration of gray seal (Halichoerus grypus) molt in the Wadden Sea, and the role of environmental conditions
Figure 2. To aid interpretation of the data, this figure presents a progression of data processing in a simulation. (A) Observations of potential absolute seal numbers on a sandbank against day of the year, using assumptions described in the text. (B) The relative proportions (prop.) of seals in each molt phase changes over time. (C) The proportion of seals in pre-visible-molt (light blue) decreases over time and the proportion in post-molt increases, the seals in early- and late-molt (green lines) peak at certain times. (D) Over time, the numbers of seals on the sandbanks that are in each visible molt phase (i.e., excludes seals in pre- and post-molt), (E) Over time, the proportions of seals in visible molt that are in early- or late-molt. (F) The proportion of seals in visible molt that were in late-molt. Note that the change over time in this proportion is linear (the horizontal dashed line indicates 50% in each stage, which occurs in this simulation on day 105).
Figure 4 in Onset and duration of gray seal (Halichoerus grypus) molt in the Wadden Sea, and the role of environmental conditions
Figure 4. The proportion of wild gray seals (given an observation quality = 1) in different molt stages over time. The proportion in pre-visible-molt decreases and that in post-molt increases over time, while numbers in early- and late-molt peak during the molt period. Data are represented by the colored dots, the lines indicate the simulation of Fig. 2c.
Figure 6 in Onset and duration of gray seal (Halichoerus grypus) molt in the Wadden Sea, and the role of environmental conditions
Figure 6. Simulations of changes in the proportion of seals in visible molt that were in latemolt, compared to the base scenario (black). These figures show the effect of shorter (red) and longer visible (orange) molt durations (A); shorter early-molt (light green) or shorter late-molt (dark green) durations (B); changes in the day of onset of molt (C); changes in the variability between individuals (SD) (D); and changes in the haul-out percentage during early- and latemolt (E). The base scenario was derived from the parameters from captive seals identified in this study, i.e., visible molt commences on average on day 99, early-molt lasts 8.2 d and late-molt lasts 8.7 d. The standard deviation that defines the variability between individuals is 15 d. This base senario assumed that the haul-out behavior is the same during early- and late-molt.
Figure 1 in Onset and duration of gray seal (Halichoerus grypus) molt in the Wadden Sea, and the role of environmental conditions
Figure 1. Aerial photograph of molting gray seals on a Wadden Sea sandbank. Seals are in pre-visible-molt (A), early-molt (B), late-molt (C), or post-molt (D). Recognizable adult males were noted separately. The quality was not always consistent due to glare or sand, and therefore seals were defined to have high (1), moderate (2), bad (3), or inadequate quality (4). The contrast of the pelage color in the true picture (upper image) was automatically selected using color select in Adobe Photoshop CS (lower image). The brown old fur was colored orange, and the grayish new fur was colored blue showing an even stronger contrast between early- and late-molt.
Figure 3 in Onset and duration of gray seal (Halichoerus grypus) molt in the Wadden Sea, and the role of environmental conditions
Figure 3. The molt progress of nine captive gray seals recorded daily in 2010. The individuals were kept at two locations (Dolfinarium and Ecomare), had different origins, ages, and sexes (see y-axis). Note that the onset and end of molt varied per individual but the duration of the phases in the visible molt (early-molt and late-molt) were similar.
Figure 1 in Body size and body conditions of two dung beetles species (Coleoptera: Scarabaeidae) related to environmental temperatures
Figure 1 Measures of body length in millimeters of individuals of Canthon rutilans cyanescens collected between August/2015 and May/2016 in (A) Santo Amaro da Imperatriz (200 m a.s.l.), whereas Sep/2105, n= 5; Oct/2015, n= 28; Nov/2015, n=6; Dec/2015, n=18; Jan/2016, n=3; Feb/2016, n=8; Mar/2016, n=7; Apr/2016, n=0; and (B) Rancho Queimado (800 m a.s.l.) in Santa Catarina state, whereas Sep/2105, n=0; Oct/2015, n=5; Nov/2015, n=0; Dec/2015, n=25; Jan/2016, n=8; Feb/2016, n=15; Mar/2016, n=7; Apr/2016, n=5. Also, measures of body length in millimeters of individuals of Dichotomius sericeus collected between November/2015 and April/2016 in two locations: (C) Santo Amaro da Imperatriz (200 m a.s.l.) Nov/2015, n=10; Dec/2015, n=56; Jan/2016, n=30; Feb/2016, n=10; Mar/2016, n=10; Apr/2016, n=0; and (D) Rancho Queimado (800 m a.s.l.) in Santa Catarina state, whereas Nov/2015, n=0; Dec/2015, n=8; Jan/2016, n=30; Feb/2016, n=29; Mar/2016, n=5; Apr/2016, n=9.
Figure 4 in Limitations of allometry, morphometry, and fluctuating asymmetry in detecting environmental stress caused by lead soil contamination in aphids under field conditions
Figure 4 Fluctuating asymmetry (mean and error deviation) observed in the antenna and tibia of Brevicoryne brassicae in the presence (Lead (Pb)) and absence (Control) of lead.
Figure 3 in Limitations of allometry, morphometry, and fluctuating asymmetry in detecting environmental stress caused by lead soil contamination in aphids under field conditions
Figure 3 Negative allometry represented by the allometric coefficients of both the antenna and tibia and their confidence intervals; the values are related to the body length ofBrevicoryne brassicae in the presence (Lead (Pb)) and absence (Control) of lead.
Figure 1 in Limitations of allometry, morphometry, and fluctuating asymmetry in detecting environmental stress caused by lead soil contamination in aphids under field conditions
Figure 1 Brevicoryne brassicae placed in a dorsal-ventral position for structure measurement. (a): Total body length (b): antenomer length (c): length of the posterior tibia. Source: the authors.
Figure 2 in Limitations of allometry, morphometry, and fluctuating asymmetry in detecting environmental stress caused by lead soil contamination in aphids under field conditions
Figure 2 Mean length and standard error of the antenna, tibia and body length of Brevicoryne brassicae in the presence (Lead (Pb)) and absence (Control) of lead.
Figure 2 in Body size and body conditions of two dung beetles species (Coleoptera: Scarabaeidae) related to environmental temperatures
Figure 2 Body fat mass (red boxes) and muscle mass (blue boxes) of individuals of (A) Canthon rutilans cyanescens collected at two locations: Santo Amaro da Imperatriz (200 m a.s.l.; n=29) and Rancho Queimado (800 m a.s.l.; n=36) in Santa Catarina state; Body fat mass (red boxes) and muscle mass (blue boxes) of individuals of (B) Dichotomius sericeus collected at two locations: Santo Amaro da Imperatriz (200 m a.s.l.; n=29) and Rancho Queimado (800 m a.s.l.; n=31) in Santa Catarina state, south of Brazil.
Figure 3 in Influence of environmental variability on the body condition of the mangrove horseshoe crab Carcinoscorpius rotundicauda from Banyuasin Estuarine, South Sumatra, Indonesia
Figure 3. The relative condition factor (Kn) of C. rotundicauda from Banyuasin Estuary Waters. There was a significant difference between Kn values for males and females at a significant level of 0.05.
Figure 2 in Influence of environmental variability on the body condition of the mangrove horseshoe crab Carcinoscorpius rotundicauda from Banyuasin Estuarine, South Sumatra, Indonesia
Figure 2. The prosoma width-weight relationship of C. rotundicauda from Banyuasin Estuary Waters. There was a different growth pattern for both sexes where males indicated negative allometric and females indicated isometric.
Fig. 2 in Unusual environmental conditions preserve a Permian mesosaur-bearing Konservat-Lagerstätte from Uruguay
Fig. 2. Mesosaurid scapulocoracoid, FC−DPV 2493, part (A) and counterpart (B), from the Early Permian Mangrullo Formation (Northeastern Uruguay) preserved in a shale surface highly bioturbated by the trace fossil Chondrites.
Fig. 1 in Unusual environmental conditions preserve a Permian mesosaur-bearing Konservat-Lagerstätte from Uruguay
Fig. 1. Generalized stratigraphic section of the Early Permian Mangrullo Formation (Northeastern, Uruguay), showing the various sedimentary facies and their corresponding fossil associations, including the "mesosaur community". Colour codes from standard Munsell Chart. Abbreviations: C, conglomerate; S, silt; FS, fine sandstone.
Fig. 9 in Unusual environmental conditions preserve a Permian mesosaur-bearing Konservat-Lagerstätte from Uruguay
Fig. 9. Exceptional preservation of internal anatomy in Mesosaurus tenuidens (FC−DPV 2109) from the Early Permian Mangrullo Formation (Northeastern Uruguay). Photograph (A) and interpretive drawing (B) of the internal mould of articulated mandibular rami, showing well preserved mandibular nerves, probably the trigeminus ramus, running along the dentary tooth series (black arrow in B), and delicate blood vessels (grey arrow in B).
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.