Sampling event

Long-term monitoring of primate, bird, and ungulate populations 2010-2022 for protected area management, Keo Seima Wildlife Sanctuary, Cambodia

最新バージョン WCS Cambodia によって公開 2022/09/20 WCS Cambodia
ホーム:
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公開日:
2022/09/20
公開者:
WCS Cambodia
ライセンス:
CC-BY 4.0

DwC-A形式のリソース データまたは EML / RTF 形式のリソース メタデータの最新バージョンをダウンロード:

DwC ファイルとしてのデータ ダウンロード 2,569 レコード English で (198 KB) - 更新頻度: as needed
EML ファイルとしてのメタデータ ダウンロード English で (18 KB)
RTF ファイルとしてのメタデータ ダウンロード English で (15 KB)

説明

Observations of 13 key species over 12 years in Keo Seima Wildlife Sanctuary, Cambodia, recorded during standardized line transect surveys. Distance sampling and density surface models are used to analyze this data and produce population estimates.

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、2,569 レコードが含まれています。

拡張データ テーブルは2 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。

Event (コア)
2569
ExtendedMeasurementOrFact 
5420
Occurrence 
5420

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。:

Agger C, Griffin O, Nuttall M, O'Kelly H (2022): Long-term monitoring of primate, bird, and ungulate populations 2010-2022 for protected area management, Keo Seima Wildlife Sanctuary, Cambodia. v1.8. WCS Cambodia. Dataset/Samplingevent. https://ipt.gbif.fr/resource?r=wcs_ksws_transect&v=1.8

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 WCS Cambodia。 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: bcaaf133-5433-46ab-b2e3-a1a9f4ce84d1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WCS Cambodia が、このリソースをパブリッシュしました。

キーワード

Occurrence; distance sampling; density surface model; Cambodia; population trends; abundance estimates; Keo Seima Wildlife Sanctuary; yellow-cheeked crested gibbon; black-shanked douc; Samplingevent

連絡先

Cain Agger
  • メタデータ提供者
  • 最初のデータ採集者
  • データ利用者
  • 連絡先
KSWS Biodiversity Monitoring Technical Advisor
WCS Cambodia
Olly Griffin
  • 最初のデータ採集者
WCS Cambodia
Matt Nuttall
  • 最初のデータ採集者
Hannah O'Kelly
  • 最初のデータ採集者

地理的範囲

Observations of species within the central area of Keo Seima Wildlife Sanctuary, Cambodia.

座標(緯度経度) 南 西 [12.056, 106.407], 北 東 [12.612, 107.299]

生物分類学的範囲

Black-shanked douc (Pygathrix nigripes), southern yellow-cheeked crested gibbon (Nomascus gabriellae), Germain's silver langur (Trachypithecus germaini), long-tailed macaque (Macaca fascicularis), northern pig-tailed macaque (Macaca leonina), stump-tailed macaque (Macaca arctoides), green peafowl (Pavo muticus), wild pig (Sus scrofa), northern red muntjac (Muntiacus vaginalis), banteng (Bos javanicus), gaur (Bos gaurus), Eld's deer (Rucervus eldii), sambar (Rusa unicolor). Records for banteng, gaur, Eld's deer, and sambar are not published here due to risk of poaching, but are available on request where appropriate.

Species Sus scrofa (Wild pig), Muntiacus vaginalis (Northern red muntjac), Pygathrix nigripes (Black-shanked douc), Pavo muticus (Green peafowl), Trachypithecus germaini (Germain's silver langur), Macaca leonina (Northern pig-tailed macaque), Nomascus gabriellae (Southern yellow-cheeked crested gibbon), Macaca fascicularis (Long-tailed macaque), Rusa unicolor (Sambar), Macaca arctoides (Stump-tailed macaque), Rucervus eldii (Eld's deer), Bos gaurus (Gaur), Bos javanicus (Banteng)

時間的範囲

開始日 / 終了日 2010-01-01 / 2022-01-01

プロジェクトデータ

Long-term technical, operational, and financial support to the Royal Government of Cambodia for effective management of Keo Seima Wildlife Sanctuary (previously Seima Biodiversity Conservation Area, Seima Protection Forest).

タイトル Keo Seima Wildlife Sanctuary
ファンデイング United States Agency for International Development (USAID), Agence Française de Développement (AFD), US Fish and Wildlife Service, GEF-5 (CAMPAS), Royal Government of Cambodia Keo Seima REDD+ (KSWS REDD+)
Study Area Description Keo Seima Wildlife Sanctuary (12.3346, 106.8418, formerly Seima Biodiversity Conservation Area and Seima Protection Forest) falls within Mondulkiri and Kratie provinces in eastern Cambodia, shares its southeastern edge with Vietnam, and has an area of 2,927 km2 (Fig. 1). The study area is the former core zone, an area of 1,880 km2 (Fig. 1). KSWS is characterized by a diverse mosaic of habitats; the southeastern area extends into the Southern Annamite Mountain Range with higher altitudinal mountainous topography, and dense evergreen and semi-evergreen forest (Evans et al. 2013). The central and western areas form the edge of the Eastern Plains Landscape, which is dominated by low altitudes and dry deciduous dipterocarp forests (O’Kelly et al. 2012; Evans et al. 2013). Complementing the altitudinal and habitat gradients are semi-natural grasslands and seasonal and permanent water bodies that together support rich biodiversity (Nuttall et al. 2017) .
研究の意図、目的、背景など(デザイン) Data were collected jointly by the Wildlife Conservation Society (WCS) and the Forestry Administration of the Royal Government of Cambodia (RGC) between 2010 and 2016, and by WCS and the Ministry of Environment of the RGC in 2018 to 2022. Square line transects of 4 km length were arranged throughout KSWS in a systematic grid with a random start point, and field teams conducted distance sampling surveys along the 40 line transects in 2010, 2011, 2013, 2014, 2016, 2018, and 2020. Field teams recorded visual observations of 11 species that were listed as threatened on the IUCN Red List, or were easily detected on line transects, or both (see Table 1 for species and name abbreviations). Laser rangefinders and compasses were used to measure distances and angles from the line transect to detected objects, which constituted either isolated individuals or spatially aggregated individuals (clusters), and cluster sizes were recorded. Distances were measured to the geometric center of clusters. Perpendicular distances from detected objects to the line transect were calculated prior to analysis. Field protocols followed standard line transect methodology outlined in Buckland et al. (2001) and were consistent between years. For further details of field protocols see Supporting Information, O’Kelly et al. (2012), and Nuttall et al. (2017).

プロジェクトに携わる要員:

Olly Griffin
  • 研究代表者
Cain Agger
Matt Nuttall
Hannah O'Kelly

収集方法

Data were collected jointly by the Wildlife Conservation Society (WCS) and the Forestry Administration of the Royal Government of Cambodia (RGC) between 2010 and 2016, and by WCS and the Ministry of Environment of the RGC in 2018 and 2020. Square line transects of 4 km length were arranged throughout KSWS in a systematic grid with a random start point, and field teams conducted distance sampling surveys along the 40 line transects in 2010, 2011, 2013, 2014, 2016, 2018, and 2020. Field teams recorded visual observations of 11 species that were listed as threatened on the IUCN Red List, or were easily detected on line transects, or both (see Table 1 for species and name abbreviations). Laser rangefinders and compasses were used to measure distances and angles from the line transect to detected objects, which constituted either isolated individuals or spatially aggregated individuals (clusters), and cluster sizes were recorded. Distances were measured to the geometric center of clusters. Perpendicular distances from detected objects to the line transect were calculated prior to analysis. Field protocols followed standard line transect methodology outlined in Buckland et al. (2001) and were consistent between years. For further details of field protocols see Supporting Information, O’Kelly et al. (2012), and Nuttall et al. (2017).

Study Extent The study area is the former core zone, an area of 1,880 km2.
Quality Control Square line transects can potentially cause detection bias around the corners, as animals on the inner side of the corner could be detected twice. Although double-counting does not in itself violate distance-sampling assumptions, bias may arise if the two sightings are non-independent, for example if the second sighting occurs because animals are still present at the location of the first sighting. To assess whether there was evidence of corner-bias in our data, we tested for differences in density of observations between corner areas and non-corner areas. The corner samples were obtained from all transect sections within 50 m of a corner, and the non-corner samples were obtained by two methods: firstly as all transect sections not within 50 m of a corner; and secondly by using 50 m transect sections around each of 1000 randomly-selected points, discarding any that overlapped with corner areas. For either method, observation density was calculated for the corner and non-corner samples and compared using a t-test. Neither method resulted in a significant difference in observation density between corner areas and non-corner areas, so no further action was taken to address corner effects. For 2010 and 2011 data, the time was not collected for observations, so linking observations to morning or evening events was not possible. Instead, the two events on a single date (morning and evening) were grouped, giving a higher total effort, and all observations for that date were assigned to the single event. This makes not difference to distance sampling analysis, but is noted to explain the apparent higher effort per event from those years. In fact, daily effort is generally equal across all years, but subdivided from 2013 onwards.

Method step description:

  1. Anon during peer-review

追加のメタデータ

目的 Data are collected in order to estimate wildlife populations and distributions, used to inform protected area management.
代替識別子 bcaaf133-5433-46ab-b2e3-a1a9f4ce84d1
https://ipt.gbif.fr/resource?r=wcs_ksws_transect