説明
Data set about the annual monitoring of the effect of herbivorism on the conservation status of endangered species Androcymbium europaeum. Since 2010, the SERPAM Department (Evaluation, Restoration and Protection of Mediterranean Agrosystems Service) of the Zaidin Experimental Station belonging to Spanish National Research Council (CSIC-EEZ), has been carrying out annual sampling to evaluate the effect of domestic and wild livestock (eg. rabbits) on the pastures inhabited by Androcymbium europaeum. A randomized block design with three treatments (type of management: rabbit and domestic herbivorism; only excluded to livestock; and excluded to rabbit and livestock) was performed. In each treatment, two types of monitoring were carried out: abundance estimation of A. europaeum by counting individuals on 50 x 50 cm squares; and plant species diversity in 2-m long transects using the modified Point-Quadrat method. This study was carried out in the "Rambla de las Amoladeras" (Almería) within the Cabo de Gata-Níjar protected area (southern Spain). The dataset describes information from 2010 to 2022. Monitoring is performed annually.
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、1,583 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。
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。:
Pérez-Luque AJ, Ramos Font ME, Tognetti-Barbieri, MJ, Montoya Roman C, Tribaldos Anda C, Robles Cruz AB (2023). Monitoring data on the effect of domestic livestock and rabbits on Androcymbium europaeum pastures. Version 1.0. Estación Experimental del Zaidín (CSIC). Samplingevent dataset. https://ipt.gbif.es/resource?r=amoladeras&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 Estación Experimental del Zaidín (CSIC)。 This work is licensed under a Creative Commons Attribution Non Commercial (CC-BY-NC 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: 340aff40-1745-4d49-bf2a-adb2899bc428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Estación Experimental del Zaidín (CSIC) が、このリソースをパブリッシュしました。
キーワード
Samplingevent; Occurrence; abundance; herbivory; species richness; grasslands; Endangered plant species; species diversity
連絡先
- 論文著者
https://orcid.org/0000-0002-1747-0469
- メタデータ提供者 ●
- 論文著者 ●
- 最初のデータ採集者 ●
- 連絡先
- データ提供者 ●
- 最初のデータ採集者 ●
- 連絡先
- データ提供者 ●
- 最初のデータ採集者 ●
- 連絡先
- データ提供者 ●
- 最初のデータ採集者
- メタデータ提供者 ●
- 最初のデータ採集者 ●
- 連絡先 ●
- 研究代表者
- 論文著者
地理的範囲
The study area belongs to the Integral Reserve of Las Marinas-Amoladeras,the main steppe zone of the Cabo de Gata-Níjar Natural Park located in Almería (southeast Spain). This area is considered hunting refuge and zoological station. The soils are limestone, poor and poorly developed (Guirado et al., 2001). Biogeographically, it belongs to the Murcian-Almerian chorological province, Almeria sector, thermo-Mediterranean semiarid-arid belt. The annual precipitation is 200 mm with strong intra- and interannual variation and the mean annual temperature is 19 ºC. The potential vegetation of the area consists of Ziziphus lotus thornscrub, but at present, shrubs of the Helianthemo-Siderition pusillae alliance dominate, reflecting the former grazing-pastoral activity, now abandoned and of which only ocassional pastoral use with sheep remains, together with current hunting activity.
| 座標（緯度経度） | 南 西 [-90, -180], 北 東 [90, 180] |
|---|
生物分類学的範囲
There are 98 taxa included in the dataset. The 5 most represented taxa in the dataset are: Androcymbium europaeum (Lange) K.Richt. (34.74%), Stipa capensis Thunb. (11.09%), Gynandriris sisyrinchium (L.) Parl. (5.64%), Filago pyramidata L. (3.51%) and Erodium chium (Burm.fil.) Willd. (2.37%). A total of 72 genus are included in the dataset, being the 5 most represented: Androcymbium (34.74%), Stipa (11.09%), Gynandriris (5.64%), Helianthemum (4.28%) and Filago (3.83%). There are 2 classes represented in the dataset: Liliopsida (57.14%) and Magnoliopsida (42.86%). A total of 21 order represented in the dataset being the 5 most represented: Liliales (34.74%), Poales (14.23%), Asterales (11.2%), Asparagales (8.14%) and Fabales (4.97%). There are 31 family included in the dataset. The 5 family most represented in the dataset are: Colchicaceae (34.74%), Poaceae (14.23%), Asteraceae (11.2%), Iridaceae (5.64%) and Fabaceae (4.87%).
時間的範囲
| 開始日 / 終了日 | 2010-03-23 / 2023-04-11 |
|---|
プロジェクトデータ
説明がありません
| タイトル | Ganadería Extensiva y Biodiversidad |
|---|---|
| 識別子 | LIFEWATCH-2019-09-CSIC-4, POPE 2014-2020 |
| ファンデイング | These data have been generated thanks to the funding of different projects, although the first samplings and the installation of the exclusion plots were funded by the Consejería de Medio Ambiente de la Junta de Andalucía through the "Ganadería Extensiva y Biodiversidad" project from 2008 to 2014. From this date on it was financed through the CSIC intramural projects "Investigaciones sobre flora forrajera bética: prospección de especies, protocolo para su establecimiento en campo y valoración nutritiva" and "Pastoralismo y Medioambiente". From 2021 onwards, funding for monitoring came from the SUMHAL project (LIFEWATCH-2019-09-CSIC-13, POPE 2014-2020). |
| Study Area Description | The study area belongs to the Integral Reserve of Las Marinas-Amoladeras,the main steppe zone of the Cabo de Gata-Níjar Natural Park) located in Almería (southern Spain). This area is considered hunting refuge and zoological station. The soils are limestone, poor and poorly developed (Guirado et al., 2001). Biogeographically, it belongs to the Murcian-Almerian chorological province, Almeria sector, thermo-Mediterranean semiarid-arid belt. The annual precipitation is 200 mm with strong intra- and interannual variation and the mean annual temperature is 19 ºC. The potential vegetation of the area consists of Ziziphus lotus thornscrub, but at present, shrubs of the Helianthemo-Siderition pusillae alliance together with Eryngio ilicifoli-Plantaginetum ovatae and Androcymbio -Tillaetum muscosae alliances dominate, reflecting the former grazing-pastoral activity, now almost abandoned and of which only ocassional pastoral use with sheep remains, together with hunting activity.now abandoned and of which only p astoral use with sheep remains, together with hunting activity. |
| 研究の意図、目的、背景など（デザイン） | To evaluate the effect of sheep and rabbits on the population of A. europaeum and its plant communities, 18 plots of 2.5 m x 2.5 m were installed in the study area. A randomized block design was followed, and consisted of 6 blocks separated between 300 and 400 m, with three different treatments or management types (one plot by treatment and block): 1) with herbivory by sheep and rabbits (G+C+), 2) excluding only sheep (G-C+) (fenced with hunting netting) and 3) excluding rabbits and sheep (G-C-) (fenced with rhomboidal netting of 4 cm of light). The density of A. europaeum in each plot and year was evaluated by counting the number of individuals in 50 cm x 50 cm fix squares, taking four squares per plot, distributed according to the four cardinal points (N, S, E and W): 24 squares per treatment (six blocks by four squares). The exclusion plots were installed in May 2010, after the first density sampling (March), thus this year should be considered as year zero, without exclusion treatments. |
プロジェクトに携わる要員:
- 研究代表者
- データ提供者
- データ提供者
- 研究代表者
収集方法
To evaluate the effect of sheep and rabbits on the population of A. europaeum and its plant communities diversity, 18 plots of 2.5 m x 2.5 m were installed in the study area. A randomized block design was followed, which consisted of 6 blocks separated between 300 and 400 m, with three different treatments or management types (one plot by treatment and block): 1) with herbivory by sheep and rabbits (G+C+), 2) excluding only sheep (G-C+) (fenced with hunting netting) and 3) excluding rabbits and sheep (G-C-) (fenced with rhomboidal netting of 4 cm of light). Two types of assessment were carried out: density of A. europaeum, and plant community evaluation.
| Study Extent | The study area belongs to the Integral Reserve of Las Marinas-Amoladeras,the main steppe zone of the Cabo de Gata-Níjar Natural Park) located in Almería (southeast Spain). This area is considered hunting refuge and zoological station. The soils are limestone, poor and poorly developed (Guirado et al., 2001). Biogeographically, it belongs to the Murcian-Almerian chorological province, Almeria sector, thermo-Mediterranean semiarid-arid belt. The annual precipitation is 200 mm with strong intra- and interannual variation and the mean annual temperature is 19 ºC. The potential vegetation of the area consists of Ziziphus lotus thornscrub, but at present, shrubs of the Helianthemo-Siderition pusillae alliance dominate, reflecting the former grazing-pastoral activity, now abandoned and of which only pastoral use with sheep remains, together with hunting activity. |
|---|---|
| Quality Control | For the abundance count, and to reduce possible bias among observers, criteria for the correct identification of individuals were established and practiced prior to sampling for each field campaign. In general, the results obtained from the beginning were quite coincident and without inter-observer bias. Each year, sampling was carried out by 2-4 observers, with at least one of them present in all the samplings. Plants for almost all species found where sampled and determined at lab. Data where carefully implemented in a database and cross-check validations were carried out. |
Method step description:
- The abundance of A. europaeum in each plot was yearly evaluated by counting the number of individuals in 50 cm x 50 cm fix squares, taking four squares per plot, distributed according to the four cardinal points (N, S, E and W): 24 squares per treatment (six blocks by four squares). The exclusion plots were installed in May 2010, after the first density and biodiversity samplings (March and April), thus this year should be considered as year zero, without exclusion treatments.
- The evaluation of the plant communities where A. europaeum lives was carried out yearly in spring, to ensure that most annual species had grow and flowered to allow a correct identification. Two fix cross transects (2 m length) were established in each plot, and using the point-intercept method (Elzinga et al. 1998), 50 points per transect were censused. The points were separated by 4 cm, and in each one of them the contacting species with a needle of 2 mm section are noted. For each transect the following variables were determined: - specific vegetation cover: percentage of soil covered by each plant species - plant species richness: number of species - diversity index (H'): Shannon index H' = - Σ pi · Ln pi - vegetation cover: percentage of soil covered by vegetation - total specific cover: sum of the specific vegetation cover of each species - musk/lichen cover: percentage of soil covered by musk or lichen - bare soil cover: percentage of bare soil
コレクションデータ
| コレクション名 | Bases de datos de seguimiento de sistemas silvopastorales mediterráneos |
|---|
書誌情報の引用
- BLANCA G., CABEZUDO B., CUETO M., FERNÁNDEZ-LÓPEZ C. Y MORALES-TORRES C. (2009) Flora Vascular de Andalucía Oriental. Vol. 4. Sevilla, España: Consejería de Medio Ambiente. Junta de Andalucía.
- BLANCA G., CABEZUDO B., HERNÁNDEZ-BERMEJO J.E., HERRERA C.M., MOLERO J., MUÑOZ J. Y VALDÉS B. (1999) Libro Rojo de la Flora Silvestre Amenazada de Andalucía. Especies en peligro de Extinción. Tomo I. Sevilla, España: Consejería de Medio Ambiente. Junta de Andalucía.
- BOZA J., ROBLES A.B., GONZÁLEZ-HERNÁNDEZ A., BARROSO F., FERNÁNDEZ-REBOLLO P. Y TERRADILLOS A. (1998) Análisis de los Pastos y Evaluación de la Capacidad Sustentadora del Parque Natural de Cabo de Gata-Nijar. Sevilla, España: SINAMBA. Consejería de Medio Ambiente, Junta de Andalucía.
- DAGET P y POISSONET J (1971). An Ecological Analysis Method of Prairies: Criteria’s of Application. Annales Agronomiques, 22, 5-41.
- RICO E. (2013) Androcymbium. En: Talavera et al (Eds) Flora iberica 20, pp 103-105. Madrid, España: Real Jardín Botánico, CSIC.
- ROBLES A.B., BARROSO F.G., GONZÁLEZ A., BOZA J. y GONZÁLEZ-REBOLLAR J.L. (2002) Propuesta metodológica para el diagnóstico del estado de los pastos en el Parque Natural de Cabo de Gata Níjar. En: Chocarro C. et al. (Eds) Producción de Pastos, Forrajes y Céspedes, pp 573-578. Lleida, España: Universitat de Lleida.
- ROBLES A.B., RAMOS M.E. Y GONZÁLEZ-REBOLLAR J.L. (2013) Efecto del herbivorismo en la conservación de la especie amenazada Androcymbium gramineum (Cav.) McBridec. En: Busqué J. et al. (Eds) Pastos y PAC 2014-2020, pp 33-40. Potes, Cantabria, España: Sociedad Española para el Estudio de los Pastos.
- TALAVERA S., ANDRÉS C., ARISTA M., FERNÁNDEZ PIEDRA M.P., RICO E., CRESPO M.B., QUINTANAR A., HERRERO A. Y AEDO C. (Eds) (2013) Liliaceae-Agavaceae. Flora iberica 20. Madrid, España: Real Jardín Botánico, CSIC.
- GUIRADO j., NAVARRO M., FERNÁNDEZ-PALACIOS J. (2001) El Parque Natural Marítimo-Terrestre de Cabo de Gata-Níjar. Un espacio excepcional. PH Boletín 37 (Especial Monográfico: Institutos de Patrimonio), 181-188.
- ELZINGA, C. L., SALZER, D. W. (1998). Measuring & monitoring plant populations. US Department of the Interior, Bureau of Land Management.
- Robles A. B., Cabeza FM, Ramos-Font, ME, & González-Rebollar, J L (2014). Effect of herbivorism on the conservation of the endangered species Androcymbium europaeum (Lange) K. Richt. Pastos, 44(2), 44-55
追加のメタデータ
| 代替識別子 | 10.15470/jpjhuu |
|---|---|
| 340aff40-1745-4d49-bf2a-adb2899bc428 | |
| https://ipt.gbif.es/resource?r=amoladeras |