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

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

Inconsistent results with this method led us to estimate re-suspension from SPM<br />

concentrations in the water column according to the tidal cycle. This second ratio method was based<br />

on SPM concentrations increasing with the tidal current in the last 50-60 meters off the seabed, while<br />

particles were mainly concentrated near bottom at slack water. Subsurface-to-bottom differences in<br />

SPM concentrations were generally calculated at mid tide and at slack waters. The subsurface mean<br />

concentrations were calculated from the first 3 metres under the pycnocline; the bottom values were<br />

the concentrations recorded at the trap depth (1.6 m off the seabed).<br />

Finally, a third attempt was made from the total particulate matter and POC fluxes measured<br />

in September in the mid-depth and bottom-moored traps. Re-suspension was calculated as the<br />

difference in fluxes recorded at the two depths, assuming settling particles all originating from the<br />

‘Grande Vasière’ surface waters (no current-driven alien inputs under the upper traps) and after<br />

checking that (i) the upper trap was not influenced by re-suspension, and (ii) the chlorophyll maximum<br />

biomass was situated over this trap.<br />

Statistical analyses<br />

Temporal and spatial fluctuations were assessed by a two-way analysis of variance (ANOVA)<br />

with season (spring or summer) and station as fixed factors, after the homogeneity of variances was<br />

tested (Cochran test). When the homogeneity hypothesis was rejected by ANOVA, Newman and<br />

Keuls a posteriori multiple-comparison tests were used to separate possible sets of homogeneous<br />

means (Clavier et al., 1995).<br />

RESULTS<br />

1- Water column<br />

Physical parameters<br />

Between-site comparisons are sometimes irrelevant since sampling may have occurred in<br />

different tide regimes, depending on the station and season, particularly in spring (e.g. during springti<strong>des</strong><br />

at A, B and F in April 2002, but during neap ti<strong>des</strong> at G; see Table 2). Mean bottom-water current<br />

on the ‘Grande Vasière’ varied according to tide coefficient, ranging from 6.01 cm.s -1 during neap<br />

ti<strong>des</strong> (coeff. 38; TROPHAL, station B) to 12.46 cm.s -1 during spring-ti<strong>des</strong> (coeff. 111-109;<br />

GASPROD, station B). However, general trends were observed: (i) bottom-water salinity and<br />

temperature appeared consistently higher in summer at all stations, except for G (Table 2); (ii) station<br />

F, under the river plumes influence, exhibited the lowest bottom-water salinity and the highest<br />

stratification index (SI) for both seasons, i.e. the highest water column stratification (either in<br />

temperature and/or salinity). The freshwater inputs in F were also underlined by colder surface-water<br />

temperature in early spring but warmer temperature in late summer, compared to the ‘Grande Vasière’<br />

stations; and (iii) water column stratification appeared quite similar in A, B, C, D and G and was<br />

higher in late summer than in spring for all the central ‘Grande Vasière’ stations (Fig. 2). The lack of<br />

spring data for the deepest station (E) does not allow to make any seasonal comparison between the<br />

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