Eric Beraud

Dr. Eric Beraud

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Research Focus & Metrics

Academic Career Length

20Years (2007-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 July 2010 in Journal of Experimental Marine Biology and Ecology
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Christine Ferrier-PagèsChristine Ferrier-Pagès
Christine Ferrier-Pagès
CRCécile Rottier
Cécile Rottier
EBEric Beraud
Eric Beraud
OLOren Levy
Oren Levy

16 May 2011 in Marine Ecology Progress Series
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Journal Article
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COC Orejas
C Orejas
Christine Ferrier-PagèsChristine Ferrier-Pagès
Christine Ferrier-Pagès
SRS Reynaud
S Reynaud
AGA Gori
A Gori
EBEric Beraud
Eric Beraud
JGJm Gili
Jm Gili
9 pages, 3 figures, 1 table.Growth rates of the cold-water corals (CWC) Madrepora oculata, Lophelia pertusa, Desmophyllum dianthus and Dendrophyllia cornigera were measured over 8 mo under controlled conditions (12°C in the dark, fed 5 times a week) by means of the buoyant weight technique. Additionally, linear growth rates were measured in M. oculata and L. pertusa for 2 and 1 yr, respectively. The weight measurements revealed growth rates, expressed as percent growth per day (mean ± SD), of 0.11 ± 0.04 for M. oculata, 0.02 ± 0.01 for L. pertusa, 0.06 ± 0.03 for D. dianthus and 0.04 ± 0.02 % d–1 for D. cornigera. Growth in M. oculata was significantly higher (p < 0.0001) than in the other 3 CWC species. For M. oculata and L. pertusa, also linear growth was recorded. These values (mean ± SD) were 0.014 ± 0.007 and 0.024 ± 0.018 mm d–1 for M. oculata and L. pertusa, respectively. This is the first study that compares the growth rates of 4 different CWC species under the same experimental conditions of water flow, temperature, salinity and food supply. These corals have different growth rates, both in terms of total weight increase and linear increase, and these growth rates can be related to interspecific physiological differences. Data on growth rates are essential to understand the population dynamics of CWC as well as the recovery capacity of these communities after disturbance.This work was funded by the European Projects HERMES (Goce-CT-2005-511234-I) and HERMIONE (Grant Agreement Number 226354) and the Spanish Project DEEP CORAL (CTM2005-07756-C02-02/MAR). This collaborative study\ud was also partly supported by the Government of the Principality of Monaco. C. Orejas was supported by a I3P postdoctoral contract from Consejo Superior de Investigaciones Científicas, CSIC (I3P-PC2006L), co-financed by the European Social Fund, and G. Tsounis by a postdoctoral fellowship by the Spanish Ministry for Science and Innovation (E-08-2007-1673618).Peer reviewe

13 January 2012 in PLOS ONE
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MHMia O. Hoogenboom
Mia O. Hoogenboom
DCDouglas Campbell
Douglas Campbell
EBEric Beraud
Eric Beraud
KDKatrina DeZeeuw
Katrina DeZeeuw
Christine Ferrier-PagèsChristine Ferrier-Pagès
Christine Ferrier-Pagès
Reef corals are heterotrophic coelenterates that achieve high productivity through their photosynthetic dinoflagellate symbionts. Excessive seawater temperature destabilises this symbiosis and causes corals to “bleach,” lowering their photosynthetic capacity. Bleaching poses a serious threat to the persistence of coral reefs on a global scale. Despite expanding research on the causes of bleaching, the mechanisms remain a subject of debate. This study determined how light and food availability modulate the effects of temperature stress on photosynthesis in two reef coral species. We quantified the activities of Photosystem II, Photosystem I and whole chain electron transport under combinations of normal and stressful growth temperatures, moderate and high light levels and the presence or absence of feeding of the coral hosts. Our results show that PS1 function is comparatively robust against temperature stress in both species, whereas PS2 and whole chain electron transport are susceptible to temperature stress. In the symbiotic dinoflagellates of Stylophora pistillata the contents of chlorophyll and major photosynthetic complexes were primarily affected by food availability. In Turbinaria reniformis growth temperature was the dominant influence on the contents of the photosynthetic complexes. In both species feeding the host significantly protected photosynthetic function from high temperature stress. Our findings support the photoinhibition model of coral bleaching and demonstrate that PS1 is not a major site for thermal damage during bleaching events. Feeding mitigates bleaching in two scleractinian corals, so that reef responses to temperature stresses will likely be influenced by the coinciding availabilities of prey for the host.

10 October 2016 in Microbial Ecology
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JWJeroen A. J. M. van de Water
Jeroen A. J. M. van de Water
RMRémy Melkonian
Rémy Melkonian
CVChristian Voolstra
Christian Voolstra
HJHoward Junca
Howard Junca
EBEric Beraud
Eric Beraud
CFChristine Ferrier-Pagès
Christine Ferrier-Pagès

1 January 2013 in Journal of Experimental Biology
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EBEric Beraud
Eric Beraud
FGFrançois Gevaert
François Gevaert
CRCécile Rottier
Cécile Rottier
Christine Ferrier-PagèsChristine Ferrier-Pagès
Christine Ferrier-Pagès
Summary: The physiological response of the scleractinian coral Turbinaria reniformis to ammonium enrichment (3 µM) was examined at 26°C as well as during a 7d increase in temperature to 31°C (thermal stress). At 26°C, ammonium supplementation slightly changed the coral physiology. It induced a decrease in symbiont density, compensated by an increase in chlorophyll content per symbiont cell. Organic carbon release was reduced, likely due to a better utilization of the photosynthesized carbon (i.e. incorporation into proteins, kept into the coral tissue). The δ15N signature of the ammonium-enriched symbionts and host tissue was also significantly decreased by 4 and 2‰ respectively, compared to the non enriched conditions, suggesting an important uptake of inorganic nitrogen by the holobiont. Under thermal stress, coral colonies that were not nitrogen enriched experienced a drastic decrease in photosynthetic and photoprotective pigments (chlorophyll a, β carotene, diadinoxanthin, diatoxanthin, peridinin), followed by a similar decrease in the rates of photosynthesis and calcification. Organic carbon release was not affected by this thermal stress. Conversely, nitrogen-enriched corals showed an increase in their pigment concentrations, which maintained rates of photosynthesis and calcification to ca. 60% and 100% of those obtained under control conditions respectively. These corals however lost more organic carbon into the environment. Overall, these results indicate that inorganic nitrogen availability can be important to determine the resilience of some scleractinian coral species to thermal stress, and can have an equivalent function as heterotrophic feeding concerning the maintenance of coral metabolism under stress conditions.

29 December 2018 in Coral Reefs
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JFJean-Pierre Fel
Jean-Pierre Fel
CLCatherine Lacherez
Catherine Lacherez
ABAlaa Bensetra
Alaa Bensetra
SMSakina Mezzache
Sakina Mezzache
EBEric Beraud
Eric Beraud
Christine Ferrier-PagèsChristine Ferrier-Pagès
Christine Ferrier-Pagès
Ultraviolet (UV) filters and preservatives, which are common constituents of sunscreens and other cosmetics, are reported as a threat for coastal coral reef ecosystems; however, few studies have assessed the effects of these compounds on coral health. This study presents the chronic effects (of measured, long-term and low concentrations) of some preservatives (ethylparaben, butylparaben), mineral UV filter (zinc oxide, ZnO) and organic UV filters (terephthalylidene dicamphor sulfonic acid, drometrizole trisiloxane, ethylhexyltriazone, butylmethoxydibenzoylmethane and 2-ethylhexyl 2-cyano-3,3-diphenylacrylate) on the maximal photosynthetic efficiency (Fv/Fm) of the symbionts associated with the scleractinian coral Stylophora pistillata. It first shows that for many organic filters, measured concentrations were significantly lower than nominal concentrations, due to the lipophilic nature of the compounds. In addition, the Fv/Fm was more sensitive to ZnO than all other sunscreen ingredients, with exposure to 90 µg L−1 ZnO for 35 d, reducing Fv/Fm by 38% compared with controls. The other UV filters tested showed no adverse effect on coral symbionts or animal tissue up to the concentration corresponding to their water solubility limit (and even above). Similarly, no adverse effect was observed in our conditions with the preservative ethylparaben, but the preservative butylparaben decreased the Fv/Fm by 25% at the highest concentration of 100 µg L−1. None of the sunscreen ingredients were as toxic to corals as the reference pollutants tributyltin, diuron and monuron, which significantly inhibited Fv/Fm at 10, 1 and 0.1 µg L−1, respectively. Overall, this study highlights the need to improve our knowledge on the in situ concentrations of UV filters and preservatives as well as their individual and combined effects on corals.