Avian malaria is absent in juvenile colonial herons (Ardeidae) but not Culex pipiens mosquitoes in the Camargue, Southern France

Apicomplexan blood parasites Plasmodium and Haemoproteus (together termed “Avian malaria”) and Leucocytozoon are widespread, diverse vector-transmitted blood parasites of birds, and conditions associated with colonial nesting in herons (Ardeidae) and other waterbirds appear perfect for their transmission. Despite studies in other locations reporting high prevalence of parasites in juvenile herons, juvenile Little Egrets (Egretta garzetta) previously tested in the Camargue, Southern France, had a total absence of malaria parasites. This study tested the hypotheses that this absence was due to insufficient sensitivity of the tests of infection; an absence of infective vectors; or testing birds too early in their lives. Blood was sampled from juveniles of four species shortly before fledging: Little Egret (n = 40), Cattle Egret (Bubulcus ibis; n = 40), Black-crowned Night-Heron (Nycticorax nycticorax, n = 40), and Squacco Heron (Ardeola ralloides; n = 40). Sensitive nested-Polymerase Chain Reaction was used to test for the presence of parasites in both birds and host-seeking female mosquitoes captured around the colonies. No malaria infection was found of in any of the heron species. Four different lineages of Plasmodium were detected in pooled samples of female Culex pipiens mosquitoes, including two in potentially infective mosquitoes. These results confirm that the absence of malaria parasites previously demonstrated in Little Egret is not due to methodological limitations. Although the prevalence of infection in mosquitoes was low, conditions within the colonies were suitable for transmission of Plasmodium. These colonial heron species may have evolved strategies for resisting malaria infection through physiological or behavioral mechanisms

Brood patch temperature during provocation of incubating common eiders in Ny-Ålesund, Svalbard

In this short note we describe the behaviour and body changes of three incubating female common eiders (Somateria mollissima) during provocation made by humans approaching the nest. The study site was near the settlement of Ny-Ålesund, Svalbard. Temperture transmitters were implanted subcutaneously at the brood patch and data recorded using a VHF receiver. We found that the female experiment exhibited a passive defence response (“freezing”), accompanied by a significant drop in brood patch temperature (0.6 °C) during provocation; this temperature drop lasted for 5 minutes. These accord with other studies of the physiological changes which the passive defence response in birds and other animals

Qu’en est-il de l’état de santé des myes au Saguenay ? Un bilan d’études sur plus d’une décennie

Le fjord du Saguenay, reconnu pour sa faune diversifiée mais aussi pour la contamination reliée aux activités industrielles et anthropiques, a fait l’objet d’un vaste programme de suivi environnemental, entrepris par notre équipe et qui visait à répondre à la question fondamentale : L’état de santé des myes s’est-il modifié dans le fjord du Saguenay ? Dans cet article de synthèse, nous avons regroupé des résultats déjà publiés sur la condition physiologique de Mya arenaria ainsi que des résultats originaux pour extraire des tendances, de façon à répertorier les sites qui s’avèrent critiques pour le bien-être physiologique de la mye. Mya arenaria (LINNÉ, 1758) ou mye des sables, choisie comme espèce sentinelle, a été échantillonnée de 1994 à 2007, en période de maturité sexuelle, dans des sites situés à l’intérieur du fjord et à son embouchure. Les objectifs de cet article sont de comparer les résultats de différents indices de condition et de suivis hormonaux et de la gamétogenèse de chaque site et en fonction des sexes, pour identifier les sites moins favorables pour la croissance et la reproduction de la mye. Nous avons démontré que les myes de Baie‑Sainte-Catherine subissent des retards de gamétogenèse tandis que les niveaux d’hormones stéroïdiennes sont très bas à Tadoussac. Ces deux sites sont soumis à des influences portuaires et à la circulation navale. Le site de Baie‑Éternité, plus en amont, se caractérise par des influences portuaires (huiles et peintures antisalissures) et une forte contamination métallique de sources urbaines et terrigènes. Anse‑aux‑Érables est un site près des influences industrielles, tandis que Anse‑Saint‑Jean est fortement influencée par les effluents municipaux et domestiques. D’amont en aval sur la rivière Saguenay, les myes des sites Anse‑à‑la‑Croix, Anse‑aux‑Érables, Petit‑Saguenay, Anse‑à‑la‑Barque, Tadoussac et Pointe‑aux‑Alouettes ont montré une croissance moindre. Les sites de Baie‑Éternité, Anse‑aux‑Érables, Anse‑Saint‑Jean et Baie-Sainte-Catherine ont un indice de maturité sexuelle moindre qu’aux autres sites, les données regroupées démontrant que ce sont les sites les plus influencés dans le fjord du Saguenay, résultats corroborés par les résultats de phagocytose. Toutes ces données démontrent que l’état physiologique de la mye répond à différents facteurs, anthropiques, biotiques et abiotiques, et que les sources ponctuelles de contamination viennent renforcer les effets négatifs de paramètres abiotiques telles la température et les conditions trophiques.The Saguenay fjord has been submitted for many years to anthropogenic influences. We surveyed this ecosystem between 1994 and 2007 to assess if Mya arenaria health status was altered by the contamination present in this ecosystem. The physiological condition of clams was determined using grouped annual data from sites at the mouth and in the Saguenay fjord. The results were analyzed according to sex and sites for all the samplings done during the active gametogenesis. The aims of this paper are to compare results of condition signs, gametogenesis stages and hormonal levels between sites and according to sex, to finally identify which sites were less favorable for the growth and reproduction of clams. We have shown that clams from Baie-Sainte-Catherine had delayed gametogenesis while those from Tadoussac showed very low steroid hormonal levels. Portuary and naval circulation influences could explain these particular results that also correspond to those from phagocytosis. Upstream in Baie‑Éternité, portuary influences (oils, anti-fouling paints) and metallic inputs from urban and terrigenous sources were reported. In Anse-aux-Érables, metallic contamination comes from industrial sources, while Anse-Saint‑Jean is influenced by sewage discharges from domestic and urban origin. From upstream to downstream, clams from Anse‑à‑la‑Croix, Anse‑aux‑Érables, Petit‑Saguenay, Anse‑à‑la‑Barque, Tadoussac and Pointe‑aux‑Alouettes showed decreased growth. Baie‑Éternité, Anse‑aux‑Érables, Anse‑Saint‑Jean and Baie-Sainte-Catherine sites, with their lower sexual maturity index and decreased phagocytosis, were shown to be the more influenced by contamination. All these data show that physiological condition of Mya arenaria reflects the combined effects of abiotic factors such as contamination, trophic conditions and site characteristics

H9N2 avian influenza virus in a Mediterranean gull

International audienc

Avian malaria is absent in juvenile colonial herons (Ardeidae) but not Culex pipiens mosquitoes in the Camargue, Southern France

Apicomplexan blood parasites Plasmodium and Haemoproteus (together termed “Avian malaria”) and Leucocytozoon are widespread, diverse vector-transmitted blood parasites of birds, and conditions associated with colonial nesting in herons (Ardeidae) and other waterbirds appear perfect for their transmission. Despite studies in other locations reporting high prevalence of parasites in juvenile herons, juvenile Little Egrets (Egretta garzetta) previously tested in the Camargue, Southern France, had a total absence of malaria parasites. This study tested the hypotheses that this absence was due to insufficient sensitivity of the tests of infection; an absence of infective vectors; or testing birds too early in their lives. Blood was sampled from juveniles of four species shortly before fledging: Little Egret (n = 40), Cattle Egret (Bubulcus ibis; n = 40), Black-crowned Night-Heron (Nycticorax nycticorax, n = 40), and Squacco Heron (Ardeola ralloides; n = 40). Sensitive nested-Polymerase Chain Reaction was used to test for the presence of parasites in both birds and host-seeking female mosquitoes captured around the colonies. No malaria infection was found of in any of the heron species. Four different lineages of Plasmodium were detected in pooled samples of female Culex pipiens mosquitoes, including two in potentially infective mosquitoes. These results confirm that the absence of malaria parasites previously demonstrated in Little Egret is not due to methodological limitations. Although the prevalence of infection in mosquitoes was low, conditions within the colonies were suitable for transmission of Plasmodium. These colonial heron species may have evolved strategies for resisting malaria infection through physiological or behavioral mechanisms

Bird Migration Routes and Risk for Pathogen Dispersion into Western Mediterranean Wetlands

Migratory movements of wild birds likely spread zoonotic infectious agents, such as avian influenza and West Nile viruses

Ornithological report 2001-2006 for the Camargue

The present ornithological report for the Camargue covers six years (2001-2006). This time-period has been marked by an accelerated global warming (the summer 2003 was particularly extreme). Owing to a constant high observation pressure, 18 new species have been recorded and many rare species have been resighted in that region (Camargue, Crau, Alpilles). Among the species or group of species which are regularly censused, the number of breeding Greater Flamingos Phoenicopterus roseus and that of wintering ducks and coots did not show any significant change. The colonial herons have continued either to increase or to fluctuate at a high level. For example, the Great White Egret Casmerodius albus has definitely settled in the delta and the Squacco Heron Ardeola ralloides has reached a new peak of 505 pairs in 2006. More efficient prospection efforts gave more precise breeding numbers for two species of solitary herons, the Great Bittern Botaurus stellaris and the Little Bittern Ixobrychus minutus. New breeding species such as the Great Cormorant Phalacrocorax carbo, White Stork Ciconia ciconia, Eurasian Spoonbill Platalea leucorodia and Greylag Anser anser increased their numbers as well as the Glossy Ibis Plegadis falcinellus of which 14 pairs has bred in 2006 and the Purple Swamphen Porphyrio porphyrio which was found for the first time breeding in 2006. The breeding species showing the most serious concern are actually the breeding gulls and terns whose figures have dramatically decreased. Without human management, this situation will even become worse in a near future. Further remarkable observations were the first case of wintering Lesser Spotted Eagle Aquila pomarina in 2001/2002, a mixed pair of Black-winged Pratincole Glareola nordmanni x Collared Pratincole G. pratincola in 2001, the settling of the Rook Corvus frugilegus in ArlesCe calendrier ornithologique couvre les six années de 2001 à 2006, une période marquée par un phénomène de réchauffement général accéléré du climat en général et par la canicule de l'été 2003 en particulier. Compte tenu de la pression d'observation élevée, 18 nouvelles espèces ont été signalées et de nombreuses espèces rares ont été revues dans la région (Camargue, Crau, Alpilles). Parmi les espèces ou groupes d'espèces qui font l'objet de recensements réguliers, les effectifs nicheurs de Flamant rose Phoenicopterus roseus de même que ceux des Anatidés et des Foulques hivernants n'appellent pas de commentaires particuliers pour ce laps de temps. Les Ardéidés coloniaux continuent soit de progresser pour certains, soit de fluctuer dans des limites qui restent élevées pour d'autres. Par exemple, la Grande Aigrette Casmerodius albus s'est installée durablement dans le delta, le Crabier chevelu Ardeola ralloides a atteint un nouveau maximum avec 505 couples en 2006. Des effectifs plus précis sont fournis pour deux espèces comme le Butoir étoilé Botaurus stellaris et le Blongios nain Ixohrychus minutus grâce à des prospections plus efficaces. Des espèces nicheuses d'installation récente comme le Grand Cormoran Phalacrocorax carho, la Cigogne blanche Ciconia ciconia, la Spatule blanche Platalea leucorodia et l'Oie cendrée Anser anser continuent de progresser de même que l'Ibis falcinelle Plegadis falcinellus dont 14 couples se sont reproduits en 2006 et la Talève sultane Porphyrio porphyrio dont la reproduction a enfin été confirmée en 2006. Parmi les espèces posant un problème grave, il faut relever les laro-limicoles nicheurs dont les effectifs se sont effondrés. Sans intervention urgente de gestion, leur situation risque d'empirer. Parmi les faits remarquables, signalons le premier cas d'hivernage de l'Aigle pomarin Aquila pomarina en 2001/2002, un couple mixte de Glaréole à ailes noires Glareola nordmanni x Glaréole à collier G. pratincola en 2001, l'installation du Corbeau freux Corvus frugilegus à Arles

Oxidative stress and immunologic responses following a dietary exposure to PAHs in Mya arenaria

<p>Abstract</p> <p>Background</p> <p>The aim of this research was to investigate oxidative stress and immune responses following a dietary polycyclic aromatic hydrocarbon (PAH) exposure in a marine bioindicator organism, the soft shell clam, <it>Mya arenaria</it>. Immune parameters in hemolymph (haemocyte number, efficiency of phagocytosis and haemocyte activity) and assessment of oxidative stress using catalase (CAT) activity and levels of malondialdehyde (MDA) performed on the digestive gland were estimated as biomarkers in clams fed in mesocosm with PAH contaminated phytoplankton. MDA levels and CAT activities were also measured <it>in situ </it>in organisms sampled in a control site (Metis Beach, Québec, Canada) as well as organisms sampled in a site receiving domestic effluents (Pointe-au-Père, Québec, Canada), to assess effects of abiotic variables related to seasonal variations and mixed contamination on the selected parameters.</p> <p>Results</p> <p>Results on immune parameters suggest that the PAHs may interfere with the maturation and/or differentiation processes of haemocytes. MDA results showed that lipid peroxidation did not occur following the exposure. The levels of CAT activity corresponded to weak antioxidant activity (no significant differences). Recovery was noted for all the immune endpoints at the end of the experiment.</p> <p>Conclusion</p> <p>Results suggest that immune parameters are early biomarkers that can efficiently detect a physiological change during a short term exposure to low concentrations of PAHs. The <it>in situ </it>survey (in the natural environment) suggested that clams from the Pointe-au-Père site did not show any oxidative stress as well as the clams contaminated in mesocosm, probably due to the low concentrations of PAHs used for this study. MDA levels increased however in organisms from Metis Beach, a response probably related to domestic effluents or parasitism.</p

Spread of Avian Influenza Viruses by Common Teal (Anas crecca) in Europe

Since the recent spread of highly pathogenic (HP) H5N1 subtypes, avian influenza virus (AIV) dispersal has become an increasing focus of research. As for any other bird-borne pathogen, dispersal of these viruses is related to local and migratory movements of their hosts. In this study, we investigated potential AIV spread by Common Teal (Anas crecca) from the Camargue area, in the South of France, across Europe. Based on bird-ring recoveries, local duck population sizes and prevalence of infection with these viruses, we built an individual-based spatially explicit model describing bird movements, both locally (between wintering areas) and at the flyway scale. We investigated the effects of viral excretion duration and inactivation rate in water by simulating AIV spread with varying values for these two parameters. The results indicate that an efficient AIV dispersal in space is possible only for excretion durations longer than 7 days. Virus inactivation rate in the environment appears as a key parameter in the model because it allows local persistence of AIV over several months, the interval between two migratory periods. Virus persistence in water thus represents an important component of contamination risk as ducks migrate along their flyway. Based on the present modelling exercise, we also argue that HP H5N1 AIV is unlikely to be efficiently spread by Common Teal dispersal only