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Structure, fonctionnement, évolution des communautés benthiques ...

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tel-00009359, version 1 - 1 Jun 2005<br />

Chapitre 3 - Fonctionnement du réseau trophique benthique de la Grande Vasière<br />

Zooplankton was collected for the entire water column with a WP2 zooplankton net (0.2 mm mesh<br />

size) and fish samples were obtained with an otter trawl.<br />

At four stations, Particulate Organic Matter (POM) was collected with a Niskin bottle twice a<br />

day for four days at depths near the fluorescence maximum (about 30 m depending on the station and<br />

the time of day ; these depths are named “POM surface”) and close to the bottom (1 – 2 m ; i.e. “POM<br />

bottom”). As a result of technical constraints of field cruises in these offshore waters all the samples<br />

were not done in the same period. The biais induced by this problem was taken in account in the<br />

analysis of results.<br />

Stable isotopes<br />

POM was collected by filtration of sea water (four liters of seawater were filtered for each<br />

sample) on precombusted Whatman GF/F filters and store frozen. Subsequently, the filters were<br />

exposed to HCl vapor for 4 h in order to remove carbonates before being placed in tin cups. The<br />

samples were analyzed for isotope ratios using a Finnigan Delta S isotope ratio mass spectrometer<br />

coupled to a Carlo Erba NA 2100 Element Analyzer.<br />

Because of the low organic matter content (< 2%) and the high rate of carbonates measured in<br />

the sediment, a total extraction of the Sediment Organic Matter (SOM) without degradation was not<br />

possible. So SOM isotopic analyse was carried out.<br />

Muscle tissue samples of megafauna, macrofauna and whole-body samples (without the<br />

digestive gut) of polychaetes were used for stable isotope analysis. After dissection, the tissue samples<br />

of all the taxa were washed carefully with distilled water in order to prevent any contamination by the<br />

carbonates. Zooplankton and suprabenthos samples were acidified (10% HCl) to remove any residual<br />

carbonates from cuticules and then rinsed with distilled water (Riera et al 2000). All samples were<br />

stored frozen individually at –20°C before freeze-drying. Each dried sample was then ground to a<br />

homogeneous powder, and 1 mg of this powder was weighed in tin capsules for stable carbon and<br />

nitrogen isotopic analyses. 13 C/ 12 C and 15 N/ 14 N ratios of fauna tissue were determined by CF-IRMS<br />

analysis using a Europa Scientific ANCA-NT 20-20 Stable Isotope Analyzer together with an ANCA-<br />

NT Solid/Liquid Preparation Module. As the samples contained more than 10% nitrogen, the CF-<br />

IRMS was operated in dual isotope mode, allowing δ 15 N and δ 13 C to be measured in the same sample.<br />

Analytical precision (Standard Deviation (SD), n=5) was 0.2‰ for both nitrogen and carbon, as<br />

estimated from standards analyzed together with the samples.<br />

Stable isotope ratios were expressed in conventional δ notation as parts per mil (‰) according<br />

to the following equation:<br />

1) δ X = [ (R sample/R standard) – 1 ] x 1,000<br />

where X is 13 C or 15 N and R is the corresponding 13 C/ 12 C or 15 N/ 14 N ratio.<br />

As δ 15 N values provide an indication of the trophic position of a consumer, the following<br />

formula was used to estimate trophic level (TL):<br />

2) TL = (δ 15 N consumer - δ 15 N mean POM) / 3.4 + 1<br />

where 3.4‰ is the assumed 15 N trophic enrichment factor according to Minagawa and Wada (1984). In<br />

a benthic ecosystem such as the Great Mud Bank (depth > 100 m), no primary production can occur<br />

227

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