説明
データ レコード
この sampling event リソース内のデータは、1 つまたは複数のデータ テーブルとして生物多様性データを共有するための標準化された形式であるダーウィン コア アーカイブ (DwC-A) として公開されています。 コア データ テーブルには、133 レコードが含まれています。
拡張データ テーブルは1 件存在しています。拡張レコードは、コアのレコードについての追加情報を提供するものです。 各拡張データ テーブル内のレコード数を以下に示します。
この IPT はデータをアーカイブし、データ リポジトリとして機能します。データとリソースのメタデータは、 ダウンロード セクションからダウンロードできます。 バージョン テーブルから公開可能な他のバージョンを閲覧でき、リソースに加えられた変更を知ることができます。
バージョン
次の表は、公にアクセス可能な公開バージョンのリソースのみ表示しています。
引用方法
研究者はこの研究内容を以下のように引用する必要があります。:
BIOSUM S.R.L, Austral S.A T, Gómez Arismendi M S (2025). Seasonal Spring Flora and Fauna Monitoring Campaign in Cuenca Marina Austral- 1 on-shore Tierra del Fuego, Argentina Total Austral. Version 1.1. TotalEnergies. Samplingevent dataset. https://ipt.mincyt.gob.ar/resource?r=informe-bio-biosum&v=1.1
権利
研究者は権利に関する下記ステートメントを尊重する必要があります。:
パブリッシャーとライセンス保持者権利者は TotalEnergies。 This work is licensed under a Creative Commons Attribution Non Commercial (CC-BY-NC 4.0) License.
GBIF登録
このリソースをはGBIF と登録されており GBIF UUID: 1edadbc8-8d0b-452c-a932-20d7e179dccbが割り当てられています。 GBIF France によって承認されたデータ パブリッシャーとして GBIF に登録されているTotalEnergies が、このリソースをパブリッシュしました。
キーワード
Samplingevent; Observation
連絡先
- 最初のデータ採集者
- Affiliate
- 連絡先
- 連絡先
- Group Biodiversity Specialist
- 連絡先
- Biodiversity Intern
地理的範囲
The survey was made within the CMA-1 on-shore area, particularly within the Cañadón Alfa deposit area.
| 座標（緯度経度） | 南 西 [-52.909, -69.609], 北 東 [-52.665, -68.604] |
|---|
生物分類学的範囲
説明がありません
| Kingdom | Plantae, Animalia, Fungi |
|---|---|
| Phylum | Bryophyta, Tracheophyta, Ascomycota, Chordata |
| Class | Bryopsida, Lecanoromycetes, Magnoliopsida, Liliopsida, Aves, Reptilia, Mammalia |
| Order | Santalales, Geraniales, Squamata, Asterales, Anseriformes, Artiodactyla, Ericales, Passeriformes, Pelecaniformes, Ranunculales, Poales, Falconiformes, Asparagales, Lecanorales, Gruiformes, Gunnerales, Pottiales, Charadriiformes, Boraginales, Lamiales, Caryophyllales, Podicipediformes, Rosales, Fabales, Brassicales, Procellariiformes, Oxalidales, Maipighiales, Apiales |
| Family | Oxalidaceae, Troglodytidae, Tyrannidae, Laridae, Plantaginaceae, Rosaceae, Procellariidae, Motacillidae, Ranunculaceae, Thraupidae, Cyperaceae, Podicipedidae, Apiaceae, Haematopodidae, Caryophyllaceae, Iridaceae, Polygonaceae, Gunneraceae, Plumbaginaceae, Calceolariaceae, Ericaceae, Scolopacidae, Poaceae, Geraniaceae, Brassicaceae, Juncaceae, Camelidae, Fabaceae, Violaceae, Threskiornithidae, Charadriidae, Liolaemidae, Parmeliaceae, Boraginaceae, Pottiaceae, Hirundinidae, Calyceraceae, Furnariidae, Schoepfiaceae, Passerellidae, Falconidae, Beberidaceae, Turdidae, Rallidae, Icteridae, Amaranthaceae, Asteraceae, Anatidae |
時間的範囲
| 開始日 / 終了日 | 2024-11-21 / 2024-11-28 |
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| 開始日 / 終了日 | 2025-02-04 / 2025-02-11 |
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収集方法
The floral component was surveyed developing a stratified systematic survey. The surveying technique was the quadrant technique, assigning a cover percentage to each especies present in the quadrant. This variable is a non-destructive variable for measuring abundance. 50 quadrants were surveyed, which were already surveyed in previous campaigns. Each quadrant had a 25 m2 surface. The faunal component was surveyed using different techniques for each animal group particularly. The study had already been stratified in 6 biotic units, each of them being surveyed particularly with a systematic sampling technique. Moreover, for some animal groups, asystematic sampling was made, but those observatios were not taken into account for the abundance calculations, only for species richness. 51 sampling stations were surveyed. Reptiles The survey was made through free active searching of individuals and the exhaustive potential microhabitat checking the only reported reptile species in CMA-1, Liolaemus magallanicus. This method was repeated for the 51 stations. In each one of them, walking transects were done, each one longer than 200 m. The counting of individuals was made by visual encounter following the Ojasti and Dallmeier criterio. During the transect survey, indirect evidence of reptile presence was registered such as caves or stool. The individuals encountered were captured, sexed and its snout-vent length (SVL) was registered. Birdlife This group was surveyed using the Brandolin, et.al (2007) counting method on each station registering every individual seen or heard for 10 minutes. Associated to each sampling station, there was a walking transect, to identify and register individual which may be hidden. Asystematic sampling was also made, through vehicular travelling of the area. Individual sighting was made through fotographic cameras with a 300 m telephoto lens and binoculars.
| Study Extent | This campaign attempted to describe the local biodiversity in Cuenca Marina Austral- 1 on-shore, both flora and fauna from its different environmental strata. The study prioritizes both the communities´ structural description, from biological indices and dominance-abundance curves, as well as the detection of non-registered especies. |
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| Quality Control | Birdlife: Before starting the survey, there was a 1-minute habituation time to ensure the birds were not warded off. The field identification of the species was made using the field and song guides from Narosky and Yzurieta (2010) and López-Lanús (2020). Moreover for the orders, families, scientific names and vernacular names for the birds observed Monteleone and Pagano (2022) and Remsen et.al (2025) was consulted. Mammals: The individual and bone remains identification was made following Olrog and Lucero (1981) Redford and Eisenberg, (1992) and the keys from Braun and Díaz (1999), Díaz (2000) and the Jayap et al. (2006), Agnolin et al. (2008), Jayap et al. (2011) and Barquez and Díaz (2020) descriptions. |
Method step description:
- Step description The survey was made following the steps on each sampling method already described.