VIS - Reference freshwater monitoring in Flanders, Belgium (post 2013)

説明

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、745 レコードが含まれています。

拡張データ テーブルは1 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。:

Van Thuyne G, Breine J, Brosens D (2023). VIS - Reference freshwater monitoring in Flanders, Belgium (post 2013). Version 1.11. Research Institute for Nature and Forest (INBO). Samplingevent dataset. https://doi.org/10.15468/klsy8u

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 Research Institute for Nature and Forest (INBO)。 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

このリソースをはGBIF と登録されており GBIF UUID: b2906713-07c4-41b1-887f-adfc0a24b3abが割り当てられています。   Belgian Biodiversity Platform 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Research Institute for Nature and Forest (INBO) が、このリソースをパブリッシュしました。

キーワード

Samplingevent; ecosystem functioning; fish-based index of biotic integrity; fish distribution; freshwater; LifeWatch; open data; River Scheldt; River Yser; River Meuse; Samplingevent

連絡先

地理的範囲

Flanders is one of the three administrative regions in the country of Belgium, located in the centre of Western Europe. The Flemish region is situated in the north of the country and covers an area of 13,522 km² (44,29% of Belgium). Belgium has a temperate maritime climate that is influenced by the North Sea and the Atlantic Ocean with substantial precipitation in all seasons. The summers are moderate and the winters are mild. The two main geographical regions of Flanders are the coastal plain in the North-West and the Central plain, further inland. With 470 inhabitants/km², Flanders is one of the most densely populated areas of Europe. The three major rivers are the River Yser, the River Scheldt, and the River Meuse. All rivers in Flanders flow into the North Sea, but only the River Yser drains directly into the sea within the jurisdiction of Flanders. The dataset comprises enclosed waters, including cut off river arms, gravel pits, ponds, natural lakes, and artificial lakes; and riverine habitats, including head streams, tributaries, and canals part of the drainage basins of the rivers Yser, Scheldt and Meuse. These three drainage basins are divided into eleven Flemish river catchments, which are divided into 102 subbasins. Overall, there are 48 unique enclosed waters sampled at 792 locations and 419 streams and rivers sampled at 1,452 locations.

生物分類学的範囲

The dataset contains 64 fish species reported from Flemish watercourses, as well as a number of non-target species (mainly crustaceans). This dataset also includes a number of typical brackish water fish species which sometimes can be found in inland water sites in proximity to the sea and/or behind the sluice gates. The class of Actinopterygii is best represented (63 species), along with one Petromyzontida (Lampetra planeri) and 7 crustaceans from the order Decapoda.

時間的範囲

収集方法

Standardized sampling methods were used as described in Belpaire et al. (2000) and Van Thuyne & Breine (2010) and are specified in the dataset as dwc:samplingProtocol. Per water body, the same method was used for each sampling event. The default method is electric fishing, but additional techniques such as gill nets, fykes, and seine netting (variable sizes) were used as well. Electric fishing was carried out using a 5 kW generator with an adjustable output voltage of 300–500 V and a pulse frequency of 480 Hz. The number of electric fishing devices and hand-held anodes used depends on the river width (Belpaire et al. 2000). In riverine environments, electric fishing was carried out on both riverbanks in upstream direction. All fishes were identified to species level, counted, and their length and weight was measured (measurement data available upon request). Since 2013, electric fishing was carried out until depletion.

Method step description:

1. Water type: Running freshwaters (width: 1.5 m, depth: < 1.30 m) Method: electrofishing with 1 anode by wading Effort: 100 m
2. Water type: Running freshwaters (width: 6 m, depth: < 1.30 m) Method: electrofishing with 2 anodes by wading Effort: 100 m
3. Water type: Running freshwaters (width: > 6 m, depth: < 1.30 m) Method: electrofishing with 2 anodes by wading Effort: 250 m with 1 anode on each riverbank, 2 m from bank
4. Water type: Running freshwaters, streaming rivers (width: > 6m, depth: > 1.30 m) Method: electrofishing with 2 anodes by boat Effort: 250 m with 2 anodes on each riverbank, 2 m from bank
5. Water type: Canals, slowly running rivers (width: > 6 m, depth: > 1.30 m) Method: electrofishing with 2 anodes by boat AND 2 fykes Effort: 250 m with 2 anodes on each riverbank, 2 m from bank AND 1 fyke for 48 hours parallel with and on both riverbanks
6. Water type: Canalized rivers with too high conductivity for electrofishing (depth: < 1.30 m) Method: seine netting Effort: 100 m, two times complete seine netting

書誌情報の引用

1. Breine, J.J.; Goethals, P.; Simoens, I.;Ercken, D.; Van Liefferinghe, C.; Verhaegen, G.; Belpaire, C.; De Pauw, N.; Meire, P.; Ollevier, F. (2001). De visindex als instrument voor het meten van de biotische integriteit van de Vlaamse binnenwateren. Instituut voor Bosbouw en Wildbeheer, Groenendaal. Eindverslag van project VLINA 9901, studie uitgevoerd voor rekening van de Vlaamse Gemeenschap binnen het kader van het Vlaams Impulsprogramma Natuurontwikkeling. 173 pp. + bijlagen.
2. EU Water Framework Directive (2000). Directive of the European parliament and of the council 2000/60/EC establishing a framework for community action in the field of water policy. Official Journal of the European Communities 22.12.2000 L 327/1.
3. Geeraerts, C.; Quataert, P. (2012a). Meetnetstrategie voor de visfauna van de Habitatrichtlijn. Revisie van het INBO-zoetwatervismeetnet. Rapporten van het Instituut voor Natuur- en Bosonderzoek 2012 (INBO.R.2012.56). Instituut voor Natuur- en Bosonderzoek, Brussel.
4. Geeraerts, C. ; Quataert, P. (2012b). Ontwerp van het Vlaams referentiemeetnet voor de visfauna. Revisie van het INBO-zoetwatervismeetnet op basis van een vraaganalyse van de informatiebehoefte van de Kaderrichtlijn Water met aandacht voor een betere afstemming tussen de ecologische meetnetten en andere monitoringsverplichtingen.Rapporten van het Instituut voor Natuur- en Bosonderzoek 2012 (rapportnr. 41). Instituut voor Natuur- en Bosonderzoek, Brussel.
5. Van Thuyne, G.; Galle, L.; Maes, Y.; De Bruyn, A.; Lambeens, I. en Breine J. (2016). Visbestandopnames in het kader van het Referentiemeetnet 2014-Bemonsteringsverslag. Rapporten van het Instituut voor Natuur- en Bosonderzoek 2016 (rapportnr. 11823901). Instituut voor Natuur- en Bosonderzoek, Brussel.
6. Van Thuyne, G.; Galle, L.; Maes, Y.; De Bruyn, A.; Lambeens, I. en Breine J. (2015). Visbestandopnames in het kader van het Referentiemeetnet 2013-Bemonsteringsverslag. Rapporten van het Instituut voor Natuur- en Bosonderzoek 2015 (rapportnr. 11299278). Instituut voor Natuur- en Bosonderzoek, Brussel.

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