Meiofauna, nematodes and associated sediment characteristics of the mangrove-colonized banks of Cayenne estuary (French Guiana) during the wet season of 2022

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、391 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。:

Spedicato A, Michaud E, Thouzeau G, Zeppilli D, Le Bec T, Gauchot C, Traunspurger W, Poullaouec M, Devesa J, Michel L, Chauvet P (2026). Meiofauna, nematodes and associated sediment characteristics of the mangrove-colonized banks of Cayenne estuary (French Guiana) during the wet season of 2022. Version 1.7. Institut Universitaire Européen de la Mer. Samplingevent dataset. https://ipt.data-terra.org/resource?r=biodiversity_meiofauna_cayenneestuary_2022&v=1.7

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 Institut Universitaire Européen de la Mer。 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: 989d55c1-1913-4e1f-bb50-414df53e02ba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Institut Universitaire Européen de la Mer が、このリソースをパブリッシュしました。

キーワード

Samplingevent; Specimen; Nematoda; Mangrove; Benthic habitats; Invertebrates; Meiofauna; French Guiana

連絡先

地理的範囲

Near Cayenne estuary river (French Guiana)

生物分類学的範囲

N/A

時間的範囲

プロジェクトデータ

Meiofauna distribution in mangroves is uneven and, when identified at phylum level, its diversity patterns are not consistent from one study area to another, and the structuring variables are different. Nematodes are the most abundant taxon in the meiofauna, and identification at genus level has proved to be more informative. The β-diversity of nematodes on a global scale is determined by the turnover between the biogeographical zones of mangrove distribution (Atlantic and Pacific) and by the nestedness between higher and lower latitudes. On a local scale, the presence or absence of mangroves, tree species and substrate type (sediment, roots or leaves) regulate nematode α-diversity and functional diversity. The micro-scale heterogeneity of mangrove habitats is rarely studied, even though it determines the functional diversity of nematodes. In Mayotte, Martinique and Guadeloupe, the heterogeneity of nematode α-diversity corresponds to the heterogeneity of sedimentary conditions, and anthropogenic activities have a major influence on nematodes. Along the Cayenne estuary, the β-diversity of nematodes is determined by marine inputs downstream and fluvial inputs upstream. Between microhabitats, diversity was highest in the forest. Appropriate redefinition of significant functional traits is required before their use, and a detailed study of a given study area is necessary for the definition of bioindicators.

プロジェクトに携わる要員:

収集方法

Samples were collected along three transects positioned at increasing distance from the sea and the town of Cayenne, thus constituting a “site” gradient. The transects were perpendicular to the water flow. - Site “Cri” (4°54’53"N, 52°20’15"W) was located at the mouth of Crique Fouillée, an inlet crossing Cayenne and draining water close to industrial, commercial, and urban activities. - Site “Conf” (4°53’49"N; 52°22’27"W) was located at the intersection between the Montsinery and Cayenne rivers, not far from the Larivot. - Site “Ty” (4°51’31"N, 52°23’59"W) was located in the Cayenne river, 10 km upstream of the estuary mouth. Three stations were sampled per transect, representing a “habitat” gradient: - “BM” on the muddy shore facing the mangrove - “F” in adult mangrove stands behind the shore - “IN” on the transitional area between BM and F, characterized by small roots. Samples were collected one hour before low tide. For each station, we sampled three sediment cores (replicates A, B, C; diameter = 12 cm, height = 20 cm). We collected sub-sample in each core with a syringe of 2 cm diameter and 10 cm length. We then sliced the small syringe in 4 layers from 0-1 cm, 1-3 cm, 3-5 cm, and 5-10 cm depth. Variables measured by core: - Grain size = core A - Meiofauna, pigments (chlorophyll a and phaeophytin a), microbial abundance and biomass, Total Carbon (TC) and Total nitrogen (TN) contents = cores A, B and C An other sediment core was dedicated to Redox potential, pH and temperature measurement. Measurement were made for each sediment layer (0-1 cm, 1-3 cm, 3-5 cm and 5-10 cm) using the WTW MultiLineTM3420 portable digital multiparameter system equipped with redox (Sensolyt ORP900P) and pH-temperature (SenTixTM 950) probes. Instrument precision was 0.01 mV (Eh) and 0.001 pH, the latter calibrated with NIST Buffers. Pore-water salinity was directly measured using a refractometer (1 ppt; practical salinity scale) after extracting a drop of filtered pore water from each layer of sediment (Michaud et al., 2022). After collection, samples for biogeochemical and grain size analyses were frozen at -80°C, while the meiofauna samples were fixed in 10% buffered formalin.

Method step description:

1. Samples for granulometry, total carbon (TC), total nitrogen (TN) and microbial analyses were freeze-dried (24h at 60°C), gently crushed to powder and homogenized for bulk sediment analyses. Grain size fractions were analyzed with a laser beam diffraction analyzer (Malvern Mastersizer-S2000). Prior to analysis, organic matter was removed and aggregated particles were deflocculated following Sperazza et al. (2004). Grain size fractions were quantified as clay, silt and sand. TC and TN were analyzed by combustion at 930°C using a CHN carbon analyzer (Flash-2000; Thermo Fisher Scientific Inc., Milan, Italy). Due to the lack of carbonates on the FG coast, the organic fraction largely dominates total carbon (Marchand et al., 2003); thus, only the total fraction (TC) was measured (Michaud et al., 2022). The molar TC:TN ratio was calculated and used as a proxy of the refractory or labile nature of the organic matter. Pigment concentrations were determined fluorometrically on a Turner 10-AU fluorometer (Turner design, San Jose, CA, USA), using an acidification step to separate phaeopigments from chlorophyll a. The Chl:Phaeo ratio was determined as an index of the state of pigment degradation. The size of bacterial and archaeal populations was estimated by quantifying the copy number of 16S rRNA genes using qPCR, according to protocols detailed in Fiard et al. (2022). Total DNA extracts quantified by fluorometric assay using a Quantifluor dsDNA kit (Promega) were used as a proxy of microbial biomass.
2. Samples for meiofauna were sieved on 32 µm and 1 mm mesh, stained with Bengal Rose and stored in 4% formaldehyde. The meiofauna was sorted directly on sieved samples using a stereomicroscope (ZEISS Stemi 508), as extraction by the Ludox density gradient method was not efficient due to the high presence of plant debris in the supernatant after centrifugation. During sorting, 150 nematodes were collected randomly per sample, or all individuals if total abundance did not reach 150. We set up to 150 the number of picked nematodes in order to have at least 100 nematodes identifiable, considering that during the mounting procedure some nematodes can be damaged or can be positioned in an unidentifiable way (Bianchelli et al., 2013; Semprucci et al., 2018; Liang et al., 2020). The nematodes were mounted on permanent slides following De Grisse (1969) and identified at genus level with a Leica DM2500 LED microscope according to Platt et al. (1985, 1988), the pictorial key of Warwick et al. (1988), Schmidt-Rhaesa et al. (2014), and the NeMys Online World Database of Nematodes (NeMys eds. 2023).

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