KG_Chui_canal_2024

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。

バージョン	公開されました。	レコード	変更の要約	DOIハンドル	最終更新者
1.2	2025-03-05 05:44:09	240	指定されていません		Aleksandr Matsyna

全1 の _start _から1までを表示する。

前にもどる1次にすすむ

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。:

Sultamuratov A (2024). Rapid Biodiversity Assessment for the Western Chui Canal Irrigation Project. Training Organization. Occurrence dataset https://doi.org/10.21373/7cgq4y accessed via GBIF.org on 2025-03-04.

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 GBIF Secretariat。 To the extent possible under law, the publisher has waived all rights to these data and has dedicated them to the Public Domain (CC0 1.0). Users may copy, modify, distribute and use the work, including for commercial purposes, without restriction.

GBIF登録

このリソースは GBIF に登録されていません。

キーワード

Occurrence; Observation

連絡先

プロジェクトデータ

Water Resources Service Agency

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).

Method step description:

1. 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.

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