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11 results for “breeding period”

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zenodo44/100

Supplementary data for "Influence of prey availability on habitat selection during the non-breeding period in a resident bird of prey"

<p><strong>Abstract</strong></p> <p>Background: For resident birds of prey in the temperate zone, the cold non-breeding period can have strong impacts on survival and reproduction with implications for population dynamics. Therefore, the non-breeding period should receive the same attention as other parts of the annual life cycle. Birds of prey in intensively managed agricultural areas are repeatedly confronted with unpredictable, rapid changes in their habitat due to agricultural practices such as mowing, harvesting, and ploughing. Such a dynamic landscape likely affects prey distribution and availability and may even result in changes in habitat selection of the predator throughout the annual cycle.</p> <p>Methods:&nbsp; In the present study, we 1) quantified barn owl prey availability in different habitats across the annual cycle, 2) quantified the size and location of barn owl breeding and non-breeding home ranges using GPS-data, 3) assessed habitat selection in relation to prey availability during the non-breeding period, and 4) discussed differences in habitat selection during the non-breeding period to habitat selection during the breeding period.</p> <p>Results: The patchier prey distribution during the non-breeding period compared to the breeding period led to habitat selection towards grassland during the non-breeding period. The size of barn owl home ranges during breeding and non-breeding&nbsp; were similar, but there was a small shift in home range location which was more pronounced in females than males. The changes in prey availability led to a mainly grassland-oriented habitat selection during the non-breeding period. Further, our results showed the importance of biodiversity promotion areas and undisturbed field margins within the intensively managed agricultural landscape.&nbsp;</p> <p>Conclusions: We showed that different prey availability in habitat categories can lead to changes in habitat preference between the breeding and the non-breeding period. Given these results we show how important it is to maintain and enhance structural diversity in intensive agricultural landscapes, to effectively protect birds of prey specialised on small mammals. Hereafter we provide the datasets and R script to reproduce the resource selection functions.</p>

opencc-by-4.0Mar 2023View details →
dryad36/100

Bird abundance data for the period 2002-2014 from the French Breeding Bird Survey (STOC)

<p>Abundance data on breeding birds from the French Breeding Bird Survey (Suivi Temporel des Oiseaux Communs, STOC), for the period 2002-2014.</p> <p>The dataset comprises 7,115 bird communities. Only 107 common species were included in the study. </p>

opencc-zeroOct 2020View details →
zenodo36/100

The distribution data of sandhill crane in Asia during non-breeding period from our fieldwork

<p>This data is the wintering distribution data of sandhill cranes collected by our research team in the fieldwork. The data has been used to publish an article in Peerj.</p>

opencc-by-4.0Aug 2019View details →
dryad36/100

Bird abundance data for the period 2002-2014 from the French Breeding Bird Survey (STOC)

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publicOct 2020View details →
dryad36/100

Data from: Claw-waving rate of male Austruca perplexa in peak and off-peak breeding periods

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publicMay 2021View details →
zenodo32/100

Distribution. Now restricted to the Channel Country of SW Queensland and the Lake Eyre Basin in NE South Australia. Descriptive notes. Head-body 95-120 mm, tail 105-160 mm, ear 23-29 mm, hindfoot 32-37 mm; weight 30-50 g. The Fawn Hopping Mouse has body form typical of hopping mice, with very long hindfeet, long tail with distal brush of longer hairs, very long ears, and large protruberant eyes. Dorsal fur is of variable color, from pale pinkish fawn to gray; ventral fur white. Unlike most other hopping mice, it has no throat pouch, but males have a glandular area of naked skin on the chest. Habitat. Occurs in low shrublands and tussock grasslands on stony ("gibber") plains and claypans. Shows marked habitat segregation from the Dusky Hopping Mouse (N. fuscus), which is closely associated with sandy substrates. Food and Feeding. The Fawn Hopping Mouse is mostly granivorous, but also eats other plant material (stems, leaves) and occasionally invertebrates. It uses succulent, salt-adapted plants around edges of claypans as a source of water. Breeding. Reproduction is probably largely opportunistic and aseasonal, with high reproductive output from near-continuous breeding after periods of high rainfall; reported littersize is 1-5, most commonly three; gestation period 38-43 days for nonlactating females. Females may mature later than other hopping mice, with reproductive maturity reached at about six months. Activity patterns. Terrestrial and nocturnal. Fawn Hopping Mice shelter during day in burrow systems that are typically simpler and shallower than those of other hopping mice. Movements, Home range and Social organization. Fawn Hopping Mice generally live singly or in small groups; typically uncommon within range, but population density may increase by an order of magnitude following periods of high rainfall. Status and Conservation. Classified as Near Threatened on The IUCN Red List. The Fawn Hopping Mouse has shown marked decline in range (estimated at greater than 50%), and presumably population size, since European settlement of Australia. This is mostlikely due to predation by the introduced house cat and Red Fox (Vulpes vulpes), and to habitat degradation associated with pastoralism. Bibliography. Brazenor (1934), Burbidge et al. (2008), Finlayson (1939), Gould (1853), Jackson & Groves (2015), Murray et al. (1999), Ogilby (1892), Thomas (1921h), Van Dyck & Strahan (2008), Waite (1898), Watts & Aslin (1981), Woinarski et al. (2014), Wood Jones (1925). in Muridae

Distribution. Now restricted to the Channel Country of SW Queensland and the Lake Eyre Basin in NE South Australia. Descriptive notes. Head-body 95-120 mm, tail 105-160 mm, ear 23-29 mm, hindfoot 32-37 mm; weight 30-50 g. The Fawn Hopping Mouse has body form typical of hopping mice, with very long hindfeet, long tail with distal brush of longer hairs, very long ears, and large protruberant eyes. Dorsal fur is of variable color, from pale pinkish fawn to gray; ventral fur white. Unlike most other hopping mice, it has no throat pouch, but males have a glandular area of naked skin on the chest. Habitat. Occurs in low shrublands and tussock grasslands on stony ("gibber") plains and claypans. Shows marked habitat segregation from the Dusky Hopping Mouse (N. fuscus), which is closely associated with sandy substrates. Food and Feeding. The Fawn Hopping Mouse is mostly granivorous, but also eats other plant material (stems, leaves) and occasionally invertebrates. It uses succulent, salt-adapted plants around edges of claypans as a source of water. Breeding. Reproduction is probably largely opportunistic and aseasonal, with high reproductive output from near-continuous breeding after periods of high rainfall; reported littersize is 1-5, most commonly three; gestation period 38-43 days for nonlactating females. Females may mature later than other hopping mice, with reproductive maturity reached at about six months. Activity patterns. Terrestrial and nocturnal. Fawn Hopping Mice shelter during day in burrow systems that are typically simpler and shallower than those of other hopping mice. Movements, Home range and Social organization. Fawn Hopping Mice generally live singly or in small groups; typically uncommon within range, but population density may increase by an order of magnitude following periods of high rainfall. Status and Conservation. Classified as Near Threatened on The IUCN Red List. The Fawn Hopping Mouse has shown marked decline in range (estimated at greater than 50%), and presumably population size, since European settlement of Australia. This is mostlikely due to predation by the introduced house cat and Red Fox (Vulpes vulpes), and to habitat degradation associated with pastoralism. Bibliography. Brazenor (1934), Burbidge et al. (2008), Finlayson (1939), Gould (1853), Jackson &amp; Groves (2015), Murray et al. (1999), Ogilby (1892), Thomas (1921h), Van Dyck &amp; Strahan (2008), Waite (1898), Watts &amp; Aslin (1981), Woinarski et al. (2014), Wood Jones (1925).

opennotspecifiedNov 2017View details →
dryad32/100

Data from: Survival varies seasonally in a migratory bird: linkages between breeding and non-breeding periods

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publicMay 2020View details →
dryad32/100

Data from: Energy status and antioxidant response in microfilariae-infected male village weavers (<em>Ploceus cucullatus</em>) across pre- and post-breeding periods in Amurum Forest Reserve

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publicDec 2025View details →
dryad32/100

Data from: critical calls: circadian and seasonal periodicity in vocal activity in a breeding colony of Panamanian golden frogs (<em>Atelopus zeteki</em>)

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publicNov 2025View details →
dryad28/100

Supplementary materials for: Female‐female aggression in a cooperatively breeding bird during the non‐breeding period: The behavioral strategy to maintain long‐term partnerships

<p>Social monogamy evolves in association with biparental care. However, males who tend to pursue multiple mating are expected to place less value on established partnerships, whereas females do the opposite to ensure males'participation in rearing offspring. Accordingly, selection is expected to favor paired females to behave aggressively towards females that approach their social mates. For species with long-term partnerships, female-female aggression commonly observed during the breeding period should also occur in the non-breeding period. We look at whether these expectations are held up by conducting a field experiment in Tibetan ground tits Pseudopodoces humilis, a cooperatively breeding bird that has lifetime monogamy and forms new pair bonds in winter. Paired but not unpaired females were more aggressive towards the same-sex than towards opposite-sex intruders experimentally introduced into the winter group territory, an indication that paired females may be protecting partnerships. Both paired and unpaired males, on the other hand, displayed aggression almost equally against intruders of both sexes, indicating a likely function in territory defense. Our work provides the first evidence for the female's role in maintaining long-term monogamy during the non-breeding period in birds, and contributes to the recent progress regarding intrasexual competition between females as a component of sexual selection.</p>

opencc-zeroAug 2020View details →
dryad28/100

Supplementary materials for: Female‐female aggression in a cooperatively breeding bird during the non‐breeding period: The behavioral strategy to maintain long‐term partnerships

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publicAug 2020View details →

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International Brain Laboratory public data

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openneuro
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Last verified 2026-04-29Open record