説明
データ レコード
この オカレンス(観察データと標本) 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、240 レコードが含まれています。
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。:
Matsyna A, Sultamuratov A (2025). Rapid Biodiversity Assessment Western Chui Canal Irrigation Project (2024). Version 1.5. Juru. Occurrence dataset. https://cloud.gbif.org/eca/resource?r=ebrd-juru-chui_canal&v=1.5
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 Juru。 This work is licensed under a Creative Commons Attribution (CC-BY 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: 5f96a6c2-f289-4e27-abbd-ed0e14a00e2bが割り当てられています。 Participant Node Managers Committee 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Juru が、このリソースをパブリッシュしました。
キーワード
Occurrence; Observation
連絡先
- 最初のデータ採集者 ●
- 連絡先
- Senior Biodiversity Specialist
- 最初のデータ採集者
- 連絡先
- Biodiversity Team Head
地理的範囲
Kyrgyzstan – Chuy Region, the area along the Great Chuy Canal from Bishkek to the border with Kazakhstan.
| 座標(緯度経度) | 南 西 [42.852, 73.514], 北 東 [42.892, 74.44] |
|---|
生物分類学的範囲
説明がありません
| Kingdom | Plantae, Animalia |
|---|---|
| Phylum | Tracheophyta, Chordata |
| Class | Magnoliopsida, Equisetopsida, Liliopsida, Aves, Mammalia |
| Order | Cucurbitales, Suliformes, Asterales, Anseriformes, Coraciformes, Solanales, Passeriformes, Pelecaniformes, Poales, Malpighiales, Myrtales, Accipitriformes, Gruiformes, Malvales, Boraginales, Charadriiformes, Lamiales, Caryophyllales, Bucerotiformes, Columbidae, Rosales, Fabales, Brassicales, Rodentia, Sapindales, Oxalidales, Apiales |
| Family | Lamiaceae, Malvaceae, Oxalidaceae, Nitrariaceae, Scrophulariaceae, Laridae, Plantaginaceae, Rhamnaceae, Corvidae, Upupidae, Elaeagnaceae, Sapindaceae, Columbidae, Rosaceae, Phalacrocoracidae, Apiaceae, Typhaceae, Ulmaceae, Polygonaceae, Sturnidae, Onagraceae, Poaceae, Scolopacidae, Brassicaceae, Juncaceae, Coraciidae, Fabaceae, Datiscaceae, Sciuridae, Boraginaceae, Accipitridae, Hirundinidae, Convolvulaceae, Rallidae, Amaranthaceae, Asteraceae, Salicaceae, Ardeidae, Cricetidae, Anatidae, Meropidae |
時間的範囲
| 開始日 / 終了日 | 2024-08-05 / 2024-08-11 |
|---|
プロジェクトデータ
This dataset was produced by Juru Ltd under the Chui Water Resource Efficiency project – financed by the European Bank for Reconstruction and Development (EBRD) – and commissioned by Water Resources Services, Ministry of Water Resources, Agriculture and Processing Industry of the Kyrgyz Republic.
| タイトル | Rapid Biodiversity Assessment for the Western Chui Canal Irrigation Project |
|---|---|
| 識別子 | EBRD |
| ファンデイング | EBRD |
プロジェクトに携わる要員:
収集方法
The field survey was carried out on August 4-12, 2024, by conventional methods of botanical research commonly used for sampling and mapping of native non-forest vegetation, recognition of floristic composition and spatial patterns of plant communities (Field geobotany, 1959–1976; Granitov, 1980; Kent, 2011).
| Study Extent | Field investigations were conducted along the Chui River, utilizing standard botanical research methodologies. A total of nine sampling areas were established at intervals of approximately 4 to 6 km along the 60 km river stretch. Additionally, three supplementary sampling areas were collected to enhance understanding of habitat diversity. |
|---|
Method step description:
- The faunal surveys along the Chui River and surrounding areas were conducted using a rapid survey approach, which, although less comprehensive than full-scale studies, provides a snapshot of the biodiversity in the region. The methodology used was consistent across the mammal, ornithological and herpetological surveys to ensure consistency in data collection and analysis. A total of 12 sample plots were systematically established along a 160 kilometer transect. These plots were strategically selected to cover a representative range of habitats along the Chui River, including riparian zones, adjacent agricultural lands and transitional areas between these habitats. Standard field equipment was used throughout the survey, including digital cameras and GPS devices. The use of digital cameras allowed accurate documentation of species, while GPS devices ensured accurate location recording of all sightings and tracks. Binoculars were also used for long-distance observations, particularly in ornithology, to minimize disturbance to the fauna. Transect walks were conducted within each sample plot, with surveyors moving slowly and systematically to maximize fauna detection. Observations were recorded both visually and acoustically. Particular attention was paid to signs of species presence such as tracks, burrows, nests and droppings. Detailed notes were made of the behavior, location and any signs of breeding or feeding of each species detected. Digital photographs were taken to aid species identification and provide a visual record. All data was geo-referenced using GPS coordinates to ensure accurate mapping of species distribution across the study area. Upon completion of the fieldwork, the data were systematically analyzed to identify patterns in species distribution and habitat use. Although this was a rapid survey, the data collected provides valuable baseline information for future, more detailed studies. Given the rapid nature of this survey, it is important to note that not all species present in the area may have been recorded, particularly those that are nocturnal, highly elusive or present in low numbers. The survey was conducted over a limited period of time and may not reflect the full diversity of the region. However, the consistent application of methodology across all disciplines provides a reliable preliminary assessment of the fauna of the Chui River area.
追加のメタデータ
| 代替識別子 | 5f96a6c2-f289-4e27-abbd-ed0e14a00e2b |
|---|---|
| https://cloud.gbif.org/eca/resource?r=ebrd-juru-chui_canal |