The consistency of satellite and in situ time series of Chlorophyll-a (Chl-a), Turbidity and Total Suspended Matters (TSM) was investigated at 17 coastal stations throughout the year 2017. These stations covered different water types, from relatively clear waters in the Mediterranean Sea to moderately turbid regions in the Bay of Biscay and the southern bight of the North-Sea. Satellite retrievals were derived from MODIS/AQUA, VIIRS/NPP and OLCI-A/Sentinel-3 spectral reflectance. In situ data were obtained from the coastal phytoplankton networks SOMLIT (CNRS), REPHY (Ifremer) and associated networks. Satellite and in situ retrievals of the year 2017 were compared to the historical seasonal cycles and percentiles, 10 and 90, observed in situ. Regarding the sampling frequency in the Mediterranean Sea, a weekly in situ sampling allowed all major peaks in Chl-a caught from space to be recorded at sea, and, conversely, all in situ peaks were observed from space in a frequently cloud-free atmosphere. In waters of the Eastern English Channel, lower levels of Chl-a were observed, both in situ and from space, compared to the historical averages. However, despite a good overall agreement for low to moderate biomass, the satellite method, based on blue and green wavelengths, tends to provide elevated and variable Chl-a in a high biomass environment. Satellite-derived TSM and Turbidity were quite consistent with in situ measurements. Moreover, satellite retrievals of the water clarity parameters often showed a lower range of variability than their in situ counterparts did, being less scattered above and under the seasonal curves of percentiles 10 and 90.
We confirm an amnesic shellfish poisoning risk associated with domoic acid production by the species Pseudo-nitzschia plurisecta and determine the toxin profile, which includes three domoic acid isomers. Although the species was reported once in European waters, along the Spanish Atlantic coast, here we describe and characterize P. plurisecta collected during the first occurrence in French Atlantic waters. Three strains (IFR-PPL-15.1, 15.2 and 15.3) were isolated from French coastal water samples in June 2015. These strains were identified and characterized by microscopic observation, molecular (ITS region sequencing and phylogenetic analysis) and metabolite (toxins and pigments) analyses. The cell shape is lanceolate and the valve contains a central interspace with uniseriate stria of oval-square poroids, each divided into 3-10 sectors. The ITS gene sequence is homologous to the original sequence available for the Spanish strain P. plurisecta. The pigment profile contains chl a, c3, c2, fucoxanthin, diatoxanthin, diadinoxanthin and traces of β,β-carotene. Results on morphology, phylogeny and pigments led to the identification of P. plurisecta and confirmed its first occurrence in French waters.
Abstract. Decadal time series of chlorophyll a concentrations sampled at high
and low frequencies are explored to study climate-induced impacts on the
processes inducing interannual variations in the initiation of the
phytoplankton growing period (IPGP) in early spring. We specifically detail
the IPGP in two contrasting coastal temperate ecosystems under the influence
of rivers highly rich in nutrients: the Bay of Brest and the Bay of Vilaine.
In both coastal ecosystems, we observed a large interannual variation in
the IPGP influenced by sea temperature, river inputs, light availability
(modulated by solar radiation and water turbidity), and turbulent mixing
generated by tidal currents, wind stress, and river runoff. We show that the
IPGP is delayed by around 30 d in 2019 in comparison with 2010. In situ observations
and a one-dimensional vertical model coupling hydrodynamics,
biogeochemistry, and sediment dynamics show that the IPGP generally does not
depend on one specific environmental factor but on the interaction between
several environmental factors. In these two bays, we demonstrate that the IPGP
is mainly caused by sea surface temperature and available light conditions,
mostly controlled by the turbidity of the system before first blooms. While
both bays are hydrodynamically contrasted, the processes that modulate the IPGP
are similar. In both bays, the IPGP can be delayed by cold spells and flood
events at the end of winter, provided that these extreme events last several
days.
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