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22 results for “godwit”

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zenodo40/100

Data from: Hidden in plain sight: migration routes of the elusive Anadyr bar-tailed godwit revealed by satellite tracking

<p><strong>Abstract</strong></p> <p>Satellite&nbsp;and&nbsp;GPS tracking&nbsp;technology&nbsp;continues&nbsp;to reveal&nbsp;new migration patterns of birds which enables comparative studies of migration strategies and distributional&nbsp;information useful in conservation. Bar-tailed godwits in the East Asian&ndash;Australasian&nbsp;Flyway <em>Limosa lapponica baueri </em>and <em>L. l. menzbieri</em> are known for their long non-stop flights, however these populations are in steep decline. A third subspecies in this&nbsp;flyway, <em>L. l. anadyrensis</em>, breeds in the Anadyr River basin, Chukotka, Russia, and is&nbsp;morphologically distinct from <em>menzbieri</em> and <em>baueri</em> based on comparison of museum&nbsp;specimens&nbsp;collected from breeding areas. &nbsp;However, &nbsp;the &nbsp;non-breeding &nbsp;distribution,&nbsp;migration route and population size of <em>anadyrensis </em>are entirely unknown. Among 24&nbsp;female bar-tailed godwits tracked in 2015&ndash;2018 from northwest Australia, the main&nbsp;non-breeding area for <em>menzbieri</em>, two birds migrated further east than the rest to breed&nbsp;in the Anadyr River basin, i.e. they belonged to the <em>anadyrensis </em>subspecies. During&nbsp;pre-breeding migration, all birds staged in the Yellow Sea and then flew to the breeding&nbsp;grounds in the eastern Russian Arctic. After breeding, these two birds migrated southwestward to stage in Russia on the Kamchatka Peninsula and on Sakhalin Island en&nbsp;route to the Yellow Sea. This contrasts with the other 22 tracked godwits that followed&nbsp;the previously described route of <em>menzbieri</em>, i.e. they all migrated northwards to stage&nbsp;in the New Siberian Islands before turning south towards the Yellow Sea, and onwards&nbsp;to northwest Australia. Since the Kamchatka Peninsula was not used by any of the&nbsp;tracked <em>menzbieri</em> birds, the 4 500 godwits counted in the Khairusova&ndash;Belogolovaya&nbsp;estuary in western Kamchatka may well be <em>anadyrensis</em>. Comparing migration patterns&nbsp;across the three bar-tailed godwits subspecies, the migration strategy of <em>anadyrensis&nbsp;</em>lies&nbsp;between&nbsp;that of <em>menzbieri </em>and <em>baueri</em>. Future&nbsp;investigations&nbsp;combining&nbsp;migration tracks with genomic data could reveal how differences in migration routines are&nbsp;evolved and maintained.</p> <p>&nbsp;</p> <p><strong>Data set</strong></p> <p>Stopping sites and migration timing of satellite-tracked bar-tailed godwits in the East Asian-Australasian Flyway</p> <p>file name: Chan et al. 2022 BARG_Stops_Timing.xlsx</p> <p>The sheet &#39;stopping_sites&#39; contains stopping sites of bar-tailed godwits&nbsp;tracked with solar Argos satellite transmitters, and their respective arrival and departure times at each site. The sheet &#39;timing&#39; contains departure and arrival times at the non-breeding and breeding sites in 2017. The transmitters were deployed in Roebuck Bay and Eighty Mile Beach, Australia, and were operating on an 8 h on and 25 h off duty cycle.&nbsp;</p> <p>&nbsp;</p> <p>Measurements of&nbsp;satellite-tracked bar-tailed godwits in the East Asian-Australasian Flyway</p> <p>file name:&nbsp;Chan et al. 2022 BARG_measurements.csv</p> <p>The datafile contains bill, wing&nbsp;and tarsus lengths&nbsp;and sex of bar-tailed godwits&nbsp;tracked with solar Argos satellite transmitters.&nbsp;The birds were&nbsp;captured&nbsp;in&nbsp;Roebuck Bay and Eighty Mile Beach, Australia.&nbsp;</p> <p>&nbsp;</p> <p><strong>Journal Article</strong></p> <p>Chan, Y.-C., Tibbitts,&nbsp;T. L., Dorofeev, D., Hassell, C. J.&nbsp;and&nbsp;Piersma T.&nbsp;(2022)&nbsp;Hidden in plain sight: migration routes of the elusive Anadyr bar-tailed godwit revealed by satellite tracking. J Avian Biol e02988.&nbsp;<a href="https://doi.org/10.1111/jav.02920">https://doi.org/10.1111/jav.02988</a></p>

opencc-by-4.0Dec 2021View details →
dryad40/100

Remote sensing and GPS tracking reveal temporal shifts in habitat use in nonbreeding Black-tailed Godwits

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publicOct 2024View details →
dryad40/100

Genetic diversity and the implications of captive rearing for a small population of Black‐tailed Godwits

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publicMar 2025View details →
dryad36/100

Geolocators lead to better measures of timing and renesting in Black-tailed Godwits and reveal the bias of traditional observational methods

<p>Long‐term population studies can identify changes in population dynamics over time. However, to realize meaningful conclusions, these studies rely on accurate measurements of individual traits and population characteristics. Here, we evaluate the accuracy of the observational methods used to measure reproductive traits in individually marked black‐tailed godwits (<i>Limosa limosa limosa</i>). By comparing estimates from traditional methods with data obtained from light‐level geolocators, we provide an accurate estimate of the likelihood of renesting in godwits and the repeatability of the lay dates of first clutches. From 2012 – 2018, we used periods of shading recorded on the light‐level geolocators carried by 68 individual godwits to document their nesting behaviour. We then compared these estimates to those simultaneously obtained by our long‐term observational study. We found that among recaptured geolocator‐carrying godwits, all birds renested after a failed first clutch, regardless of the date of nest loss or the number of days already spent incubating. We also found that 43% of these godwits laid a second replacement clutch after a failed first replacement, and that 21% of these godwits renested after a hatched first clutch. However, the observational study correctly identified only 3% of the replacement clutches produced by geolocator‐carrying individuals and designated as first clutches a number of nests that were actually replacement clutches. Additionally, on the basis of the observational study, the repeatability of lay date was 0.24 (95% CI 0.17 – 0.31), whereas it was 0.54 (95% CI 0.28 – 0.75) using geolocator‐carrying individuals. We use examples from our own and other godwit studies to illustrate how the biases in our observational study discovered here may have affected the outcome of demographic estimates, individual‐level comparisons, and the design, implementation, and evaluation of conservation practices. These examples emphasize the importance of improving and validating field methodologies and show how the addition of new tools can be transformational.</p>

opencc-zeroMar 2020View details →
dryad36/100

Earthworm abundance and availability does not influence the reproductive decisions of black-tailed godwits in an agricultural grassland

<ol> <li>Maintaining the biodiversity of agricultural ecosystems has become a global imperative. Across Europe, species that occupy agricultural grasslands, such as Black-tailed Godwits (<i>Limosa limosa limosa</i>), have undergone steep population declines. In this context, there is a significant need to both determine the root causes of these declines and identify actions that will promote biodiversity while supporting the livelihoods of farmers.</li> <li>Food availability, and specifically earthworm abundance (Lumbricidae), during the pre-breeding period has often been suggested as a potential driver of godwit population declines. Previous studies have recommended increasing the application of nitrogen to agricultural grasslands to enhance earthworm populations and aid agricultural production. Here we test whether food availability during the pre-breeding period affects when and where godwits breed.</li> <li>Using large-scale surveys of food availability, a long-term mark-recapture study, focal observations of foraging female godwits, and tracking devices that monitored godwit movements, we found little evidence of a relationship between earthworm abundance and the timing of godwit reproductive efforts or the density of breeding godwits. Furthermore, we found that the soils of intensively managed agricultural grasslands may frequently be too dry for godwits to forage for those earthworms that are present.</li> <li>The increased application of nitrogen to agricultural grasslands will therefore likely have no positive effects on godwit populations. Instead, management efforts should focus on increasing the botanical diversity of agricultural grasslands, facilitating conditions that prevent hardening soils, and reducing the populations of generalist predators.</li> </ol>

opencc-zeroDec 2021View details →
dryad36/100

Dataset for: Breeding populations of Marbled Godwits and Willets have high annual survival and strong site fidelity to managed wetlands

<p><span>The Prairie Pothole Region of central Canada supports a diverse community of breeding waterbirds but many species have declining populations and the demographic mechanisms driving the declines remain unknown. We conducted a 7-year field study during 1995–2001 to investigate the demographic performance of Marbled Godwits (<em>Limosa</em> <em>fedoa</em>) and Willets (<em>Tringa</em> <em>semipalmata</em>) breeding in managed wetlands near Brooks, Alberta. Mark-recapture analyses based on Cormack-Jolly-Seber models revealed that the annual rates of apparent survival for Marbled Godwits (phi-hat = 0.934 </span><span>±</span><span> 0.015SE) and Willets (phi-hat = 0.849 </span><span>±</span><span> 0.018SE) are among the highest rates of survivorship reported for any breeding or nonbreeding population of large-bodied shorebirds. Our estimates of life expectancy for males were comparable to longevity records in godwits (E-hat = 17.3 years </span><span>±</span><span> 5.8SE vs. 25-29+ years) and Willets (E- hat = 7.7 </span><span>±</span><span> 1.5SE vs. 10+ years). The two species both showed strong breeding site fidelity but differed in rates of mate fidelity.  Pairs that reunited and males that switched mates usually nested &lt;300 m from their previous nests whereas females that switched mates usually moved longer distances &gt;1.1 to 1.5 km. Returning pairs usually reunited in godwits (85%) but not in Willets (28%), possibly because of species differences in adult survival or patterns of migration. Baseline estimates of annual survival for banded-only birds will be useful for evaluating the potential effects of new tracking tags or the environmental changes that have occurred during the past 20 years. Conservation strategies for large-bodied shorebirds should be focused on reduction of exposure to anthropogenic mortality because low rates of natural mortality suggest that losses to collisions at breeding sites or harvest at nonbreeding areas are likely to cause additive mortality.</span></p>

opencc-zeroDec 2022View details →
dryad36/100

Flexibility in the face of climate change? A rapid and dramatic shift toward later spring migration in Hudsonian godwits (Limosa haemastica)

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publicJun 2025View details →
dryad36/100

Dataset for: Breeding populations of Marbled Godwits and Willets have high annual survival and strong site fidelity to managed wetlands

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publicDec 2022View details →
dryad36/100

Data from: High dispersal ability versus migratory traditions: Fine-scale population structure and post-glacial colonization in bar-tailed godwits

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publicJun 2025View details →
dryad36/100

Geolocators lead to better measures of timing and renesting in Black-tailed Godwits and reveal the bias of traditional observational methods

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publicMar 2020View details →
dryad36/100

Earthworm abundance and availability does not influence the reproductive decisions of black-tailed godwits in an agricultural grassland

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publicDec 2021View details →
dryad36/100

Daily and seasonal use of vocalizations by nesting black-tailed godwits

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publicSep 2024View details →
dryad32/100

Black-tailed Godwit abundancies across key European breeding habitats

<p>The endangered continental Black-tailed Godwit (<em>Limosa limosa limosa</em>) is a migratory ground-nesting wader breeding in a wide variety of open, wet habitats across Europe. Conservation research has concentrated on the causes of population decline, but we know surprisingly little about whether any resources limit local breeding populations and, if so, whether these are resources for the adults or the chicks. We collected data from 63 key breeding sites in five countries across Europe to test whether, after correcting for differences in surveyed areas, the size of Godwit breeding populations was related to environmental variables (vegetation biomass, soil moisture) or food resources for adult birds (soil invertebrates) or chicks (vegetation dwelling arthropods) measured during different times of the reproductive cycle. We found the number of Godwit territories to be positively related to arthropod abundance during the chick-hatching period. We found additional, weaker support for a positive relation between Godwit territory numbers and the abundance of soil-dwelling invertebrates (mostly earthworms) at clutch laying, but not at chick-hatching. These relationships were observed across countries, while we found little support for relationships within countries, possibly due to the smaller range in conditions that exist within countries. Both vegetation growth and soil moisture weren't related to Godwit territory numbers. Our results suggest that food abundance for chicks, and to a lesser extent adult birds, are key factors determining the size of local Godwit breeding populations. Conservation management aiming to enhance local Godwit populations should therefore consider the impacts of management strategies on the arthropod prey of chicks.</p>

opencc-zeroDec 2021View details →
dryad32/100

Data from: When Siberia came to the Netherlands: the response of continental black-tailed godwits to a rare spring weather event

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publicJun 2015View details →
dryad32/100

Black-tailed Godwit abundancies across key European breeding habitats

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publicMar 2023View details →
zenodo28/100

Figure 7 from: Han Y-D, Mironov SV, Min G-S (2022) Two new species of feather mites (Acariformes, Astigmata) from the black-tailed godwit, Limosa limosa (Charadriiformes, Scolopacidae), in Korea. ZooKeys 1088: 81-97. https://doi.org/10.3897/zookeys.1088.80307

Figure 7 Phyllochaeta limosae sp. nov., legs A genu, tibia and tarsus I of male B genu, tibia and tarsus II of male C tibia and tarsus III of male D tibia and tarsus IV of male E tibia and tarsus III of female F tibia and tarsus IV of female.

opencc-by-4.0Mar 2022View details →
zenodo28/100

Figure 4 from: Han Y-D, Mironov SV, Min G-S (2022) Two new species of feather mites (Acariformes, Astigmata) from the black-tailed godwit, Limosa limosa (Charadriiformes, Scolopacidae), in Korea. ZooKeys 1088: 81-97. https://doi.org/10.3897/zookeys.1088.80307

Figure 4 Alloptes species A–DAlloptes (Conuralloptes) neolimosae sp. nov. E–HA. (C.) limosae. A, E hysteronotal shield of males B, F opisthosomal lobes of males C, G opisthosomal lobes of females D, H setae h2 of males.

opencc-by-4.0Mar 2022View details →
zenodo28/100

Figure 3 from: Han Y-D, Mironov SV, Min G-S (2022) Two new species of feather mites (Acariformes, Astigmata) from the black-tailed godwit, Limosa limosa (Charadriiformes, Scolopacidae), in Korea. ZooKeys 1088: 81-97. https://doi.org/10.3897/zookeys.1088.80307

Figure 3 Alloptes (Conuralloptes) neolimosae sp. nov., details A opisthosoma of male, dorsal view B leg I of male C leg II of male D leg III of male E tibia and tarsus IV of male F leg III of female G leg IV of female.

opencc-by-4.0Mar 2022View details →
zenodo24/100

Figure 5 from: Han Y-D, Mironov SV, Min G-S (2022) Two new species of feather mites (Acariformes, Astigmata) from the black-tailed godwit, Limosa limosa (Charadriiformes, Scolopacidae), in Korea. ZooKeys 1088: 81-97. https://doi.org/10.3897/zookeys.1088.80307

Figure 5 Phyllochaeta limosae sp. nov., male A dorsal view B ventral view.

opencc-by-4.0Mar 2022View details →
zenodo24/100

Figure 6 from: Han Y-D, Mironov SV, Min G-S (2022) Two new species of feather mites (Acariformes, Astigmata) from the black-tailed godwit, Limosa limosa (Charadriiformes, Scolopacidae), in Korea. ZooKeys 1088: 81-97. https://doi.org/10.3897/zookeys.1088.80307

Figure 6 Phyllochaeta limosae sp. nov., female A dorsal view B ventral view.

opencc-by-4.0Mar 2022View details →

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