Dataset of butterfly monitoring in Sierra Nevada (Spain)

サンプリング イベント
最新バージョン Sierra Nevada Global-Change Observatory (UGR-JA) により出版 12月 17, 2021 Sierra Nevada Global-Change Observatory (UGR-JA)

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 10,369 レコード English で (8 MB) - 更新頻度: annually
EML ファイルとしてのメタデータ ダウンロード English で (23 KB)
RTF ファイルとしてのメタデータ ダウンロード English で (21 KB)

説明

This data set comprises information collected in field about the monitoring of the butterfly communities of Sierra Nevada since 2008. The data set has been compiled in up to 20 different locations, where butterfly communities estimations have been carried out following the internationally standardised line transect method. The data have been collected from the months of March to October with a variable periodicity between sites and between years. Usually, the periodicity has approached a sampling every two weeks. The data collection has always been carried out in suitable climatic conditions. The community of butterflies of Sierra Nevada is of high interest at European level given the values of diversity detected. In total, 101,424 individuals belonging to 102 species and 1 subspecies have been detected, distributed among 64 genera and 5 different families. The sampled habitats include aquatic systems, autochthonous scot pine forests, high mountain grasslands, high mountain meadows, high mountain scrubland, holm oak forests, lowland crops, lowland scrublands, mid mountain grasslands, mid mountain scrubland, mountain crops, pine plantations and pyrenean oak forests.

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、10,369 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)
10369
Occurrence 
34137
MeasurementOrFacts 
4852

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。:

Barea-Azcón J M (2021): Dataset of butterfly monitoring in Sierra Nevada (Spain). v1.2. Sierra Nevada Global Change Observatory. Andalusian Environmental Center, University of Granada, Regional Government of Andalusia. Dataset/Samplingevent. https://doi.org/10.15470/tc3gdq

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 Sierra Nevada Global-Change Observatory (UGR-JA)。 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: d7a3df60-e856-438b-851d-74653ef6c0d2が割り当てられています。   GBIF Spain 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Sierra Nevada Global-Change Observatory (UGR-JA) が、このリソースをパブリッシュしました。

キーワード

Butterflies; high Mediterranean mountain; Protected Areas; Sierra Nevada; global change.; Samplingevent

連絡先

José Miguel Barea-Azcón
  • メタデータ提供者
  • 最初のデータ採集者
  • 連絡先
  • Technician
Agencia de Medio Ambiente y Agua. Department of Agriculture, Livestock, Fisheries and Sustainable Development. Regional Government of Andalusia
  • C/ Minerva 7. Edificio Zeus III, local
18014 Granada
Granada
ES
Andrea Ros Candeira
  • 連絡先
  • Research Assistant
Laboratorio de Ecología (iEcolab), Instituto Interuniversitario de Investigación del Sistema Tierra en Andalucía (CEAMA), Universidad de Granada
  • Avenida del Mediterráneo s/n
18006 Granada
Granada
ES
  • +34 958 249748

地理的範囲

Sierra Nevada (SE Spain) is one of the southernmost highest mountain ranges of Europe. It comprises an elevation range from 270 to 3,492 m a.s.l. and it extends along 100 km from west to east in parallel to the Mediterranean coast line, with a notable increase of aridity towards the eastern sector. Sierra Nevada presents a notable environmental heterogeneity, not only in its elevational gradient, but also in its different orientations and in the west-east gradient. The five Mediterranean bioclimatic belts are represented here: thermo, meso, supra, oro and crioro-Mediterranean. A forest belt occupies good part at the middle and lower elevations and presents an uneven state of transformation, while certain extensions of holm oaks still persist (on siliceous environments and also on carbonate soils), relictic Pyrenean oak forests and some native pine forests of Pinus sylvestris and Pinus pinaster, the presence of more than 30,000 ha of reforestation pine forests is also noteworthy. Above the tree line there are 30,000 ha of typical mediterranean mountain scrubland mainly compounded by species of the genus Genista, Juniperus, Berberis and Hormatophila among others. On the upper belts, rocky landscapes defined by recent glacial events alternates with high mountain grasslands and 74 glacial lakes distributed in an elevation range situated between 2,600 and 3,100 m a.s.l. The high mountain area comprises more than 30 summits that reach an elevation above 3,000 m a.s.l. During more than the half of the year, these areas remain under a snow cover and this fact conditions a good part of the ecological processes there. The high mountain ecosystem of Sierra Nevada holds a huge number of plant and animal endemism, representing a hotspot within the mediterranean hotspot. Sierra Nevada hold some of the higher protections figures for a natural area in Spain and in Europe, so it was declared as a Natural Park since 1989 and as a National Park since 1999, is also designated as a UNESCO Biosphere Reserve (since 1986), as a Natura 2000 network site (since 2006) and holds the distinctive Green List awarded by the IUCN in recognition of good management practices.

座標(緯度経度) 南 西 [36.937, -3.609], 北 東 [37.154, -2.95]

生物分類学的範囲

This dataset includes a total of 34,137 occurrence records of the order Lepidoptera, which compile the butterfly counts by species and section. In total, 101,424 individuals of butterflies were recorded since 2008, belonging to 102 species and 1 subspecies. There are 64 genera and 5 families represented in this dataset.

Family Pieridae, Lycaenidae, Hesperiidae, Papilionidae, Nymphalidae

時間的範囲

開始日 / 終了日 2008-07-07 / 2020-03-08

プロジェクトデータ

Since 2007, Sierra Nevada Global-Change Observatory has undergone an ambitious project promoted by the Environmental and Regional Planning Council of the Regional Government of Andalusia, with the scientific coordination of the University of Granada-Andalusian Environmental Centre (IISTA, Interuniversity Institute of Research of Earth Systems in Andalusia) and with the collaboration of the Spanish National Park Service, in order to develop a monitoring and information management program. The design of the monitoring program was based on the conceptual framework and the thematic categories proposed by the GLOCHAMORE initiative (GLObal CHAnge in MOuntain REgions http://mri.scnatweb.ch/en/projects/glochamore), under the auspices of UNESCO. This monitoring program is based on specific questions concerning the global-change impact, the functioning of the natural systems, and their foreseeable responses under the new scenarios of change. Monitoring methodologies were defined to evaluate both the state of the key ecological functions, such as the structure of the main ecosystems in Sierra Nevada, and the possible impact of global change on Sierra Nevada. Sierra Nevada Global-Change Observatory promotes the collaboration between the different teams belonging to various institutions (researchers from the University of Granada and other academic institutions at the national and international levels, as well as decision makers) in order to plan transversal work with integrative objectives.

タイトル Sierra Nevada Global-Change Observatory
識別子 OBSNEV
ファンデイング "Convenio de Colaboración entre la Consejería de Medio Ambiente de la Junta de Andalucía y la Universidad de Granada para el desarrollo de actividades vinculadas al Observatorio de Cambio Global de Sierra Nevada, en el marco de la Red de Observatorios de Cambio Global de Andalucía”
Study Area Description Sierra Nevada (SE Spain) is one of the southernmost highest mountain ranges of Europe. It comprises an elevation range from 270 to 3,492 m a.s.l. and it extends along 100 km from west to east in parallel to the Mediterranean coastline, with a notable increase of aridity towards the eastern sector. Sierra Nevada presents a notable environmental heterogeneity, not only in its elevational gradient, but also in its different orientations and in the west-east gradient. The five Mediterranean bioclimatic belts are represented here: thermo, meso, supra, oro and crioro-Mediterranean. A forest belt occupies good part at the middle and lower elevations and presents an uneven state of transformation, while certain extensions of holm oaks still persist (on siliceous environments and also on carbonate soils), relictic Pyrenean oak forests and some native pine forests of Pinus sylvestris and Pinus pinaster, the presence of more than 30,000 ha of reforestation pine forests is also noteworthy. Above the tree line there are 30,000 ha of typical Mediterranean mountain scrubland mainly compounded by species of the genus Genista, Juniperus, Berberis and Hormatophila among others. On the upper belts, rocky landscapes defined by recent glacial events alternates with high mountain grasslands and 74 glacial lakes distributed in an elevation range situated between 2,600 and 3,100 m a.s.l. The high mountain area comprises more than 30 summits that reach an elevation above 3,000 m a.s.l. During more than the half of the year, these areas remain under a snow cover and this fact conditions a good part of the ecological processes there. The high mountain ecosystem of Sierra Nevada holds a huge number of plant and animal endemism, representing a hotspot within the Mediterranean hotspot. Sierra Nevada hold some of the higher protections figures for a natural area in Spain and in Europe, so it was declared as a Natural Park since 1989 and as a National Park since 1999, is also designated as a UNESCO Biosphere Reserve (since 1986), as a Natura 2000 network site (since 2006) and holds the distinctive Green List awarded by the IUCN in recognition of good management practices.

プロジェクトに携わる要員:

収集方法

Sampling method consists of a walk transect based on the method proposed by Pollar and Yates (1994) that is the most widely used method in this type of studies. This method consists in counting every butterfly along the transect within a 5 meters band at each side of the observer and also 5 meters above and ahead. Transects average length were 1,900 meters (300 to 3,270 m). The butterflies were mainly visually identified, but a butterfly net has been used in the cases when the visual identification was not possible. Every captured butterfly was released at the same place where it had been catched once it was identified. All the identifications were made at the species levels except for some individuals that only could be identified at Genus level.

Study Extent The network of transects in Sierra Nevada is distributed from 700 to 3,100 m a.s.l. in nine types of ecosystems, broadly characterized as: aquatic systems (occupying less than 1% of the transects), grasslands, rocky high mountains ecosystems (27%), high mountain wet pastures (4%), high mountain scrub dominated by high mountain scrublands (35%), holm oak woods (2%), medium mountain pastures (9%), medium mountain scrub (8%), coniferous plantations (less than 1%), pyrenean oak forests (11%) and Pinus sylvestris autochthonous pine forests (2%).
Quality Control A) Digitalization and storage: all data is stored in a normalized database in the Information System of Sierra Nevada Global-Change Observatory, whose data entry form includes several validation rules. B) Taxonomic validation: Lepidoptera scientific names were checked with the updated checklist of the European Butterflies (Wiemers et al., 2018), available in GBIF (Maes et al., 2020). C) Standardisation: the standardisation to Darwin Core was done according to the practices recommended by the TDWG guidelines (https://dwc.tdwg.org/terms/).

Method step description:

  1. The original database is stored in the Information System of Sierra Nevada Global-Change Observatory.
  2. The dataset was standardised to the Darwin Core structure (Wieczorek et al., 2012) as sampling event data. It contains, specifically: 10,369 records of events (1,725 parent events and 8,644 child events), 34,137 records of occurrences, and 4,852 records of associated measurements (wind, cloud cover, air temperature). The parent events refer to the transect sampling whereas the child events correspond to each section sampling (transects are divided into sections, and butterflies are counted separately in each section). The Darwin Core elements included in the Event Core are: eventID, parentEventID, modified, language, institutionCode, ownerInstitutionCode, datasetName, license, continent, country, countryCode, verbatimLocality, eventDate, year, month, day, eventTime, samplingProtocol, sampleSizeValue, sampleSizeUnit, minimumElevationInMeters, maximumElevationInMeters, habitat, decimalLatitude, decimalLongitude, geodeticDatum, georeferenceRemarks, footprintWKT. For the Occurrence Extension are: occurrenceID, catalogNumber, collectionCode, eventID, eventDate, recordedBy, organismQuantity, organismQuantityType, lifeStage, basisOfRecord, scientificName, taxonRank, kingdom, phylum, class, order, family, genus, specificEpithet, infraSpecificEpithet, scientificNameAuthorship. For the Measurement or Fact Extension table, the Darwin Core elements included are: measurementID, eventID, measurementType, measurementValue, measurementUnit, measurementMethod.
  3. The resulting dataset was published through the Integrated Publishing Toolkit of the Spanish node of the Global Biodiversity Information Facility (GBIF) (http://ipt.gbif.es).

書誌情報の引用

  1. Maes, D., Wiemers, M., Verovnik, R., Warren, M., Brosens, D., & Desmet, P. (2020). National checklists and red lists for European butterflies [Data set]. Research Institute for Nature and Forest (INBO). https://doi.org/10.15468/YE7WHJ https://doi.org/10.15468/YE7WH
  2. Olivares, F.J., Barea-Azcón, J.M., Pérez-López, F.J., Tinaut, J.A. y Henares, I. (2012). Mariposas diurnas de Sierra Nevada. Consejería de Medio Ambiente, Junta de Andalucía.
  3. Pollard, E. & Yates, T. J. (1994). Monitoring butterflies for ecology and conservation. Chapman & Hall, London.
  4. Sevilleja, C.G., van Swaay, C.A.M., Bourn, N., Collins, S., Settele, J., Warren, M.S., Wynhoff, I. and Roy, D.B. (2019). Butterfly Transect Counts: Manual to monitor butterflies. Report VS2019.016, Butterfly Conservation Europe & De Vlinderstichting/Dutch Butterfly Conservation, Wageningen.
  5. Van Swaay, C.A.M., Brereton, T., Kirkland, P. & Warren, M.S. (2012) Manual for Butterfly monitoring. Report VS2012.010, De Vlinderstichting/Dutch Butterfly Conservation, Butterfly Conservation UK & Butterfly Conservation Europe, Wageningen.
  6. Wieczorek, J., Bloom, D., Guralnick, R., Blum, S., Döring, M., Giovanni, R., Robertson, T., & Vieglais, D. (2012). Darwin core: An evolving community-developed biodiversity data standard. PLoS ONE, 7(1). https://doi.org/10.1371/journal.pone.0029715 https://doi.org/10.1371/journal.pone.0029715
  7. Wiemers, M., Balletto, E., Dincă, V., Fric, Z. F., Lamas, G., Lukhtanov, V., Munguira, M. L., van Swaay, C. A. M., Vila, R., Vliegenthart, A., Wahlberg, N., & Verovnik, R. (2018). An updated checklist of the European Butterflies (Lepidoptera, Papilionoidea). ZooKeys, 811, 9-45. https://doi.org/10.3897/zookeys.811.28712 https://doi.org/10.3897/zookeys.811.28712

追加のメタデータ

代替識別子 10.15470/tc3gdq
d7a3df60-e856-438b-851d-74653ef6c0d2
https://ipt.gbif.es/resource?r=butterflies