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279 results for “Austral”

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dryad36/100

Raw data for: Novel food resources and conservation of ecological interactions between the Andean Araucaria and the Austral parakeet

<p><span>In fragile ecosystems, the introduction of exotic species could alter some ecological processes. The Austral parakeet (<em>Enicognathus</em> <em>ferrugineous</em>) shows close ecological and evolutionary relationships with the Andean Araucaria (<em>Araucaria</em> <em>araucana</em>), so any alteration in these interactions may have negative consequences for both partners and for ecosystem functioning and structure. We conducted extensive roadside surveys to estimate the abundance of parakeets in the northern Patagonian Andes over four years and recorded the food plants consumed by foraging flocks. The use of native habitats and humanized areas like villages and farms was influenced by Araucaria seed crop. In masting years, the large seed crop allowed a massive use of this resource during the non-breeding season, and even during the breeding season. The exploitation of exotic plants was minor in the masting year, but became predominant in non-masting years, especially during the non-breeding season. This feeding switch towards exotic plants primarily arose because the low Araucaria seed crop in non-masting years is entirely consumed just after production by domestic and wild exotic mammals living in Araucaria forests year-round, thus forcing the displacement of parakeets towards anthropic habitats to exploit exotic plants. Given the degradation of the remaining Andean Araucaria forests due to the impact of exotic mammals on the ecological interaction between Araucaria and Austral parakeets, ambitious programs to exclude or reduce the density of these alien mammals, including livestock, are warranted. </span></p>

opencc-zeroOct 2022View details →
zenodo36/100

Bacterial and phytoplankton abundances by flow cytometry - collected from the Southern Ocean in the austral summer of 2016/2017, during the Antarctic Circumnavigation Expedition.

<p>Seawater surface samples (5 m) were collected every 6 hours from the ship&rsquo;s underway pump. In addition, vertical profiles (6 depths, generally from 5 to 100-150 m) were sampled from CTD casts using a SBE 911 Plus attached to a rosette of 24 12-L PVC Niskin bottles. This dataset presents the abundances of high-DNA containing and low-DNA containing bacteria, pico and nanophytoplankton from seawater samples collected from the ship&rsquo;s underway pump and CTDs.&nbsp; Samples were fixed with paraformaldehyde and glutaraldehyde and stored at -80&ordm;C. In the lab, they were thawed, and one replicate, for bacteria, was stained with SYBR-Green and counted in a Cube 8 flow cytometer (SYSMEX PARTEC) based on green fluorescence. Another replicate was analyzed without staining for phytoplankton, and counted based on the red and orange autofluorescences. Samples were collected around the Southern Ocean on the R/V Akademik Tryoshnikov in the austral summer of 2016/2017, as part of the Antarctic Circumnavigation Expedition (ACE).</p>

opencc-by-4.0Jun 2024View details →
zenodo36/100

Raw multibeam bathymetry data collected around Southern Thule, part of the South Sandwich Island chain in the Southern Ocean on board the R/V Akademik Tryoshnikov during the austral summer of 2016/2017 as part of the Antarctic Circumnavigation Expedition (ACE).

<p><strong>Dataset abstract</strong></p> <p>An ELAC Nautik 3020 multibeam echo sounder with a 20 kHz transducer mounted on the hull of the R/V Akademik Tryoshnikov, was used to collect multibeam bathymetry data during the Antarctic Circumnavigation Expedition (ACE). This particular dataset was collected around Southern Thule, part of the South Sandwich Island chain in the Southern Ocean in the austral summer of 2016/2017.</p> <p>Bathymetry data were used live during the cruise to look for suitable locations where benthic trawling and remotely-operated vehicle deployments could take place, rather than to undertake specific bathymetric surveys.</p> <p>This raw dataset is provided without calibration information for the surface sound velocity or instrumentation itself and should be used with due caution.</p> <p><strong>Dataset contents</strong></p> <ul> <li>lineYYYYDDmonHHMMSS.xse, data file, proprietary format</li> <li>lineYYYYDDmonHHMMSS.ssv, data file, ASCII</li> <li>location.hydrostar, ancillary file, ASCII</li> <li>data_file_header.txt, metadata, text</li> <li>README.txt, metadata, text</li> </ul> <p><strong>Dataset license</strong></p> <p>This raw multibeam bathymetry dataset is made available under the Creative Commons Attribution 4.0 International License (CC BY 4.0) whose full text can be found at https://creativecommons.org/licenses/by/4.0/</p>

opencc-by-4.0Oct 2019View details →
zenodo36/100

Raw multibeam bathymetry data collected around Bouvetoya in the South Atlantic Ocean on board the R/V Akademik Tryoshnikov during the austral summer of 2016/2017 as part of the Antarctic Circumnavigation Expedition (ACE).

<p><strong>Dataset abstract</strong></p> <p>An ELAC Nautik 3020 multibeam echo sounder with a 20 kHz transducer mounted on the hull of the R/V Akademik Tryoshnikov, was used to collect multibeam bathymetry data during the Antarctic Circumnavigation Expedition (ACE). This particular dataset was collected around Bouvetoya in the South Atlantic Ocean in the austral summer of 2016/2017.</p> <p>Bathymetry data were used live during the cruise to look for suitable locations where benthic trawling and remotely-operated vehicle deployments could take place, rather than to undertake specific bathymetric surveys.</p> <p>This raw dataset is provided without calibration information for the surface sound velocity or instrumentation itself and should be used with due caution.</p> <p><strong>Dataset contents</strong></p> <ul> <li>lineYYYYDDmonHHMMSS.xse, data file, proprietary format</li> <li>location.hydrostar, ancillary file, ASCII</li> <li>data_file_header.txt, metadata, text</li> <li>README.txt, metadata, text</li> </ul> <p><strong>Dataset license</strong></p> <p>This raw multibeam bathymetry dataset is made available under the Creative Commons Attribution 4.0 International License (CC BY 4.0) whose full text can be found at https://creativecommons.org/licenses/by/4.0/</p>

opencc-by-4.0Oct 2019View details →
zenodo36/100

TABLE 2 in Studies in Austral Bryaceae (Bryopsida). IV. New records from the Falkland Islands (Islas Malvinas), with a phytogeographic analysis of the family

<p>TABLE 2. &mdash; Sorenson&rsquo;s coefficient of similarity among six regions in the southern hemisphere for the moss family Bryaceae. The larger the percent similarity the more similar floras are to each other.Abbreviations: <b>FI</b>, Falkland Islands; <b>NZ</b>, South Island and offshore islands of New Zealand with some extensions to the North Island; <b>SA</b>, South Africa; <b>SAM</b>, southern South America; <b>SI</b>, subantarctic islands; <b>TAS</b>, Tasmania, with extensions to southeast Australia.</p><table><tbody><tr><th></th><th><b>SAM</b></th><th><b>FI</b></th><th><b>NZ</b></th><th><b>TAS</b></th><th><b>SA</b></th><th><b>SI</b></th></tr></tbody><tbody><tr><th>SAM</th><td>100</td><td>77.4</td><td>64</td><td>51</td><td>41</td><td>54.4</td></tr><tr><th>FI</th><td>&ndash;</td><td>100</td><td>75</td><td>58.7</td><td>38.3</td><td>54</td></tr><tr><th>NZ</th><td>&ndash;</td><td>&ndash;</td><td>100</td><td>92.5</td><td>40.8</td><td>75</td></tr><tr><th>TAS</th><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>100</td><td>55.6</td><td>68.1</td></tr><tr><th>SA</th><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>100</td><td>38.8</td></tr><tr><th>SI</th><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>100</td></tr></tbody></table>

opencc-by-4.0Nov 2022View details →
zenodo36/100

APPENDIX 1 in Studies in Austral Bryaceae (Bryopsida). IV. New records from the Falkland Islands (Islas Malvinas), with a phytogeographic analysis of the family

<p>APPENDIX 1. &mdash; List of Bryaceae species from the southern hemisphere used in the study. Although <i>Bryum chrysoneuron</i> M&uuml;ll.Hal. is reported from the subantarctic Macquarie Island it is likely misidentified (R. Seppelt, pers. comm. 2021). Its removal from the analyses would not affect the results. <i>Bryum gilliesii</i> Hook. and <i>B. platyphyllum</i> M&uuml;ll.Hal. are placed within <i>Plagiobryoides</i> J.R.Spence as they are likely members of that genus. <i>Bryum lamprocarpum</i> M&uuml;ll.Hal. is placed within <i>Plagiobryum</i> Lindb. as it may be a member of that genus. Neither combination was made.</p><table><tbody><tr><th><b>Genus</b></th><th>Species</th><th><b>Tierra del</b> <b>Fuego/</b> <b>S. Patagonia</b></th><th><b>Falklands</b></th><th><b>New Zealand</b></th><th><b>Tasmania</b></th><th>South Africa</th><th><b>Sub</b> Islands</th><th><b>Antarctica</b></th></tr></tbody><tbody><tr><th><i>Anomobryum</i></th><td><i>A. drakensbergense</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>A. julaceum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td></tr><tr><th><i>Brachymenium</i></th><td><i>B. magellanicum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th><i>Bryum</i></th><td><i>B. argenteum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td></tr><tr><td><i>B. badium</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. barnesii</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. caespiticium</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. dichotomum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td></tr><tr><td><i>B. funkii</i></td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. harriotii</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>B. microimbricatum</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. miserum</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. pabstianum</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. rhizoblastum</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. sabuletorum</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>B. sauteri</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><th><i>Imbribryum</i></th><td><i>I. alpinum</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>I. australe</i></td><td>1</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>Bryum chrysoneuron</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>I. clavatum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>I. crassinervium</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>I. laevigatum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>I. subapiculatum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>I. orthotheciellae</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><th><i>Ochiobryum</i></th><td><i>O. blandum</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><th><i>Plagiobryoides</i></th><td><i>Bryum gilliesii</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. orbiculatifolia</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td></tr><tr><td><i>Bryum platyphyllum</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th><i>Plagiobryum</i></th><td><i>Bryum lamprocarpum</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. novae -seelandiae</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. zierii</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th><i>Ptychostomum</i></th><td><i>P. altisetum</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. bimum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. chorizodontum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. cernuum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. compactum</i></td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. creberrimum</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. dicarpum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. donatii</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. eatonii</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. gayanum</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. inclinatum</i></td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td></tr><tr><td><i>P. kerguelense</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. lamprochaete</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. mucronatum</i></td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. nivale</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td></tr><tr><td><i>P. orthothecium</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. pallens</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. pallescens</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>1</td></tr><tr><td><i>P. pauperculum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. pseudotriquetrum</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td></tr><tr><td><i>P. tenuidens</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. turbinatum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. vernicosum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>P. weigelii</i></td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>P. zeballosicum</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th><i>Rhodobryum</i></th><td><i>R.</i> cf. <i>roseodens</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th><i>Rosulabryum</i></th><td><i>R. billarderii</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>1</td><td>&ndash;</td></tr><tr><td><i>R. capillare</i></td><td>1</td><td>1</td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>R. flaccidum</i></td><td>&ndash;</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>R. macrophyllum</i></td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><td><i>R. microrhodon</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th></th><td><i>R. perlimbatum</i></td><td>1</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th></th><td><i>R. puconense</i></td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th></th><td><i>R. rubens</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th></th><td><i>R. subtomentosum</i></td><td>&ndash;</td><td>&ndash;</td><td>1</td><td>1</td><td>&ndash;</td><td>&ndash;</td><td>&ndash;</td></tr><tr><th>Species</th><td></td><td>38</td><td>28</td><td>26</td><td>21</td><td>11</td><td>22</td><td>7</td></tr><tr><th>Endemics</th><td></td><td>11</td><td>3</td><td>2</td><td>2</td><td>1</td><td>4</td><td>0</td></tr></tbody></table>

opencc-by-4.0Nov 2022View details →
zenodo36/100

A dataset for tracking the activity and abundance of Bogong moths at Mt Gingera, ACT in the austral summer of 2020-2021

<p>This dataset contains images captured using wildlife cameras outside Bogong moth aestivation caves on Mt Gingera, ACT in the austral summer of 2020-2021. The images contain motion blurs from insects (predominantly Bogong moths&nbsp;<em>Agrotis infusa</em>)&nbsp;flying past the cameras, allowing for the measurement of Bogong moth wingbeat frequency, activity, and abundance using the Camfi software (<a href="https://github.com/J-Wall/camfi">https://github.com/J-Wall/camfi</a>).</p>

opencc-by-4.0Jun 2021View details →
zenodo36/100

A dataset for tracking the activity and abundance of Bogong moths at Mt Kosciuszko, NSW in the austral summer of 2020-2021

<p>This dataset contains images captured using wildlife cameras outside Bogong moth aestivation caves on Mt Kosciuszko, NSW in the austral summer of 2020-2021. The images contain motion blurs from insects (predominantly Bogong moths&nbsp;<em>Agrotis infusa</em>)&nbsp;flying past the cameras, allowing for the measurement of Bogong moth wingbeat frequency, activity, and abundance using the Camfi software (<a href="https://github.com/J-Wall/camfi">https://github.com/J-Wall/camfi</a>).</p>

opencc-by-4.0Jun 2021View details →
zenodo36/100

A dataset for tracking the activity and abundance of Bogong moths at Mt Kosciuszko, NSW in the austral summer of 2019-2020

<p>This dataset contains images captured using wildlife cameras outside Bogong moth aestivation caves on Mt Kosciuszko, NSW in the austral summer of 2019-2020. The images contain motion blurs from insects (predominantly Bogong moths&nbsp;<em>Agrotis infusa</em>)&nbsp;flying past the cameras, allowing for the measurement of Bogong moth wingbeat frequency, activity, and abundance using the Camfi software (<a href="https://github.com/J-Wall/camfi">https://github.com/J-Wall/camfi</a>).</p>

opencc-by-4.0Jun 2021View details →
dryad36/100

Daily variation and repeatability of advertisement calls in an austral temperate forest frog under controlled conditions

Open the record for dataset details and reuse information.

publicAug 2024View details →
dryad36/100

Raw data for: Novel food resources and conservation of ecological interactions between the Andean Araucaria and the Austral parakeet

Open the record for dataset details and reuse information.

publicOct 2022View details →
zenodo32/100

One-minute average cruise track and ship velocity of the Antarctic Circumnavigation Expedition (ACE) undertaken during the austral summer of 2016/2017.

<p><strong>Dataset abstract</strong></p> <p>The ship&#39;s cruise track, velocity, course over ground and heading at one-minute resolution for all five legs of the Antarctic Circumnavigation Expedition (ACE) are derived from a combination of:<br> - the latitude/longitude record of the Quality-checked, one-second cruise track for 21.12.2016 to 11.04.2017.<br> - the latitude/longitude record of the Uncorrected inertial navigation dataset (one-second resolution) for 27.11.2016 to 21.12.2016<br> - the latitude/longitude record of the raw meteorological data (30-second resolution) from 17.11.2016 to 27.11.2016<br> - where no latitude/longitude record at one-second resolution is available and the ship&#39;s velocity was above 2 meters per second, the three-second resolution record of the true and relative wind speed and direction, as well as the heading are used to re-calculate the ship&#39;s velocity under the assumption that the course of the ship equalled the heading.<br> Basic filtering are applied to remove erroneous observations before the data are averaged to a one-minute resolution.</p> <p><strong>Dataset contents</strong></p> <ul> <li>cruise-track-1min-legs0-4.csv, data file, comma-separated values</li> <li>data_file_header, metadata, text format</li> <li>README.txt, metadata, text format</li> <li>ace-cruise-track-1min-legs0-4-change-log.txt, metadata, text format</li> </ul> <p><strong>Change log</strong></p> <p><strong>v1.1</strong> - Added additional data coverage from 2016-11-17 - 2016-11-22 inclusive. Updated README.txt with information about data coverage. Added this change_log file.</p> <p><strong>v1.0</strong> - Initial release of averaged cruise track dataset.</p> <p><strong>Dataset license</strong></p> <p>This one-minute averaged cruise track and velocity dataset is made available under the Creative Commons Attribution 4.0 International License (CC BY 4.0) whose full text can be found at https://creativecommons.org/licenses/by/4.0/</p>

opencc-by-4.0Apr 2020View details →
dryad32/100

Frozen verses: Antarctic minke whales (Balaenoptera bonaerensis) call predominantly during austral winter --data_minke

<p>The recent identification of the bio-duck call as Antarctic minke whale (AMW) vocalization allows the use of passive acoustic monitoring to retrospectively investigate year-round spatial- temporal patterns in minke whale occurrence in ice-covered areas. Here, we present an analysis of AMW occurrence patterns based on a 9-year passive acoustic dataset (2008– 2016) from 21 locations throughout the Atlantic sector of the Southern Ocean (Weddell Sea). AMWs were detected acoustically at all mooring locations from May to December, with the highest presence between August and November (bio-duck calls present at more than 80% of days). At the southernmost recording locations, the bio-duck call was present up to 10 months of the year. Substantial inter-annual variation in the seasonality of vocal activity correlated to variation in local ice concentration. Our analysis indicates that part of the AMW population stays in the Weddell Sea during austral winter. The period with the highest acoustic presence in the Weddell Sea (September–October) coincides with the timing of the breeding season of AMW in lower latitudes. The bio-duck call could therefore play a role in mating, although other behavioural functions of the call cannot be excluded to date.</p>

opencc-zeroOct 2020View details →
dryad32/100

Data from: Assessing the effects of human activities on the foraging opportunities of migratory shorebirds in Austral high-latitude bays

Human presence at intertidal areas could impact coastal biodiversity, including migratory waterbird species and the ecosystem services they provide. Assessing this impact is therefore essential to develop management measures compatible with migratory processes and associated biodiversity. Here, we assess the effects of human presence on the foraging opportunities of Hudsonian godwits (Limosa haemastica, a trans-hemispheric migratory shorebird) during their non-breeding season on Chiloé Island, southern Chile. We compared bird density and time spent foraging in two similar bays with contrasting disturbance levels: human presence (mostly seaweed harvesters accompanied by dogs) was on average 0.9±0.4 people per 10 ha in the disturbed bay, whereas it was negligible (95% days absent) in the non-disturbed bay. Although overall abundances were similar between bays, godwit density was higher in the non-disturbed bay throughout the low tide period. Both days after the start of the non-breeding season and tidal height significantly affected godwit density, with different effects in either bay. Time spent foraging was significantly higher in the non-disturbed bay (86.5±1.1%) than in the disturbed one (81.3±1.4%). As expected, godwit density significantly decreased with the number of people and accompanying dogs in the disturbed bay. Our results indicate that even a low density of people and dogs can significantly reduce the foraging opportunities of shorebirds. These constraints, coupled with additional flushing costs, may negatively affect godwits' pre-migratory fattening. Hence, as a first step we suggest limiting human presence within bays on Chiloé to 1 person per 10 ha and banning the presence of accompanying dogs in sensitive conservation areas.

opencc-zeroDec 2018View details →
zenodo32/100

FIGURE 4. Calcinus aff. sirius Morgan, 1991 in Hermit crabs of the genus Calcinus Dana, 1851 (Decapoda: Anomura: Diogenidae) from the Austral Islands, French Polynesia, with description of a new species

FIGURE 4. Calcinus aff. sirius Morgan, 1991, ov. Ψ 5.5 mm, Rapa Island, 100 m (MNHN Pg 6395): a, distal part of propodus, and dactyl of left P2, outer face; b, left P2, outer face; c, left P3, outer face. Scale bars 1 mm.

opennotspecifiedDec 2003View details →
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FIGURE 5 in Hermit crabs of the genus Calcinus Dana, 1851 (Decapoda: Anomura: Diogenidae) from the Austral Islands, French Polynesia, with description of a new species

FIGURE 5. Left chela: a, Calcinus albengai n. sp., holotype ɗ 3.8 mm, Marotiri Isles, 100–120 m (MNHN Pg 6359); b, Calcinus aff. sirius, ov. Ψ 5.5 mm, Rapa Island, 100 m (MNHN Pg 6395). Scale bars 1 mm.

opennotspecifiedDec 2003View details →
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FIGURE 2. Calcinus albengai n in Hermit crabs of the genus Calcinus Dana, 1851 (Decapoda: Anomura: Diogenidae) from the Austral Islands, French Polynesia, with description of a new species

FIGURE 2. Calcinus albengai n. sp.: a–f, holotype ɗ 3.8 mm, Marotiri Isles (MNHN Pg 6359); g, paratype ov. Ψ 3.0 mm, Neilson Reef, 150 m (MNHN Pg 6361); h, ɗ 3.5 mm, Rapa Island, 53 m (MNHN Pg 6382). a, anterior portion of shield and cephalic appendages; b, left chela and carpus, outer face; c, right chela and carpus, outer face; d, left P2 of deep­water variant, outer face; e, left P3 of deep­water variant, outer face; f, posterior portion of telson, ventral view; g, left chela and carpus, outer face; h, left P3 of shallow­water variant, outer face. Scale bars 1 mm.

opennotspecifiedDec 2003View details →
zenodo32/100

FIGURE 1 in Hermit crabs of the genus Calcinus Dana, 1851 (Decapoda: Anomura: Diogenidae) from the Austral Islands, French Polynesia, with description of a new species

FIGURE 1. Live coloration (except b, taken several weeks after preservation): a, Calcinus albengai n. sp., deep­water variant, holotype ɗ 3.8 mm, Marotiri Isles, 100–120 m (MNHN Pg 6359); b, Calcinus albengai n. sp., shallow­water variant, ɗ 3.5 mm, Rapa Island, 53 m (MNHN Pg 6382); c, Calcinus gouti Poupin, 1997, ɗ 5.0 mm, Tikehau, 15 m (UF 1349); d, Calcinus aff. sirius Morgan, 1991, 1 ov. Ψ 5.5 mm, Rapa Island, 100 m (MNHN Pg 6395). Photographs by L. Albenga (a, b), G. Paulay (c), and J. Poupin (d).

opennotspecifiedDec 2003View details →
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FIGURE 3. Calcinus gouti Poupin, 1997 in Hermit crabs of the genus Calcinus Dana, 1851 (Decapoda: Anomura: Diogenidae) from the Austral Islands, French Polynesia, with description of a new species

FIGURE 3. Calcinus gouti Poupin, 1997, ɗ 5.0 mm, Tikehau Atoll, 15 m (UF 1349): a, anterior portion of shield and cephalic appendages; b, left chela and carpus, outer face; c, right chela and carpus, outer face; d, right P2, outer face; e, right P3, outer face; f, posterior portion of telson, ventral view. Scale bars 1 mm.

opennotspecifiedDec 2003View details →
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FIGURE 5 in New polychaete species collected during the expeditions ANDEEP I, II, and III to the deep Atlantic sector of the Southern Ocean in the austral summers 2002 and 2005 — Ampharetidae, Opheliidae, and Scalibregmatidae

FIGURE 5. Pseudoscalibregma papilia sp. nov. A. entire animal, B. anterior segments, C. posterior parapodium, D. furcate chaetae, E. pygidium.

opennotspecifiedDec 2008View details →

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Last verified 2026-04-29Open record

OpenNeuro

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openneuro
neuroscienceopenPublished datasets are available on demand over the internet.
Last verified 2026-04-29Open record