Biodiversity surveys conducted for Maneah Linsan Powerline EIA

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、1,252 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。:

Biotope (2024). Biodiversity surveys conducted for Maneah Linsan EIA. Version 1.0. Biotope. Occurrence dataset. https://ipt-biotope.gbif.fr/resource?r=field_surveys_maneah_linsan&v=1.0

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 Biotope。 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: d1c25c97-2a1b-4324-9bf4-2c0c316c38b9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Biotope 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; Mammals; Birds; Guinea; Plants; Observation

連絡先

地理的範囲

The project covers the prefectures of Coyah and Kindia, crossing a total of 10 sub-prefectures: Maneah, Kouriah, Mambia, Samayah, Friguiagbe, Damankania, Kindia Centre, Kolente, Sougueta and Linsan.

生物分類学的範囲

説明がありません

時間的範囲

プロジェクトデータ

As part of its strategic development plan, Electricité de Guinée (EDG) is planning to build a 225 kV high-voltage power line linking the Manéah transformer station (existing, just outside Conakry) and the Linsan transformer station (under construction as part of the CLSG and OMVG interconnection projects). The project also includes the construction of a new transformer substation in the Kouriah area, in the industrial park currently under development. Eventually, this line will be extended to the Koukoutamba dam currently under construction.

プロジェクトに携わる要員:

収集方法

The mammals data in this dataset were collected as part of the chimpanzee-specific supplementary study for the initial status of the Manéah Linsan high-voltage power line project. The mammals data were collected using 22 camera traps located in the area of influence of the powerline (around 5km). The camera traps were set on April 23 to 30, 2022, on locations where chimpanzees pass, rest or feed. They were placed against a tree, generally about 50 cm high. The traps were set as follows: 2 photos and 1 video; time between shots: 5 seconds (minimum); video duration: 10 seconds; motion detector sensitivity: medium. Each camera installed was numbered (Codes: ML001 to ML022) and geo-referenced. The cameras were installed (April 23-30, 2022) for one month, after which they were retrieved (June 13-30, 2022) for data analysis.

Regarding flora, 20 survey sites were selected in the main study area, according to the following criteria:
- To be representative of all the natural and modified habitats highlighted by the preliminary study of aerial images and the bibliographical information gathered;
- Target original habitats with potential botanical importance (home to species of high heritage value), i.e.: gallery forests, patches of dense forest, wooded savannah/open forest, shrub savannah, old fallow (transitional environments with dominant pioneer species), bowé, and rocky environments (with seasonal seepage zones); and
- Be accessible to experts.
Two methods were used for data collection: (1) the 25mx25m plot method and (2) the random transect method. The plot method consists of delimiting a 25mx25m square within the site and surveying the vegetation, by stratum, within this square. Random transects were carried out within each site, in order to describe and photograph the main habitats present (Habitat, Species, Family, Biological type, Abundance, Status, Condition, Degradation index). Particular attention was paid to endangered and/or endemic plant species, which were recorded and herbariumed.

Regarding birds, the purpose of the ornithological inventory was to draw up a non-exhaustive list of bird species present in the study area, with priority given to species that could trigger the critical habitat criterion as defined by the World Bank's NES n°6 (mainly endemic/limited-range and/or threatened species) potentially present in the area. Particular attention was paid to these species during the inventories, to ensure that the project took the best possible account of the issues associated with these species, whose ecology makes them highly sensitive to this type of infrastructure. Potential breeding habitats were also sought (cliffs, tall trees, etc.) and inventoried.
In order to capture the variety of bird assemblages associated with the different habitat types present in each of the study areas, 35 sampling sites were identified to encompass the heterogeneity of the environments present. Sampling consisted in following survey itineraries through the sites, actively selecting those places where there was information or indications of the presence of the species of interest, or where there were no such indications, areas potentially suitable for their habitat.
The approach involved walking and driving along transects in different sectors, making georeferenced visual and auditory observations. For the auditory observations, 10-minute listening points were defined (2 to 10 in number, depending on the relief of the sectors sampled). These listening points, 250-300 metres apart, were marked by a period of replay of the species' songs lasting around 30 seconds. As far as possible, unfavorable weather conditions were avoided and the surveys were carried out during the species' peak activity hours, usually the early hours of the morning and the late hours of the afternoon.

Method step description:

1. See sampling description

追加のメタデータ