Ciguatera fish poisoning (CFP) is a human foodborne intoxication caused by ingestion of tropical fishes contaminated with the potent polyether toxins known as ciguatoxins (CTXs). These toxins are issued from Gambierdiscus species of dinoflagellates. Herbivorous fish accumulate these toxins in their musculature and viscera after ingesting dinoflagellates. Epidemiological studies showed that CFP has been present in areas between 35 degrees North and 35 degrees South latitude, mainly, Indo-pacific and Caribbean areas, but not in waters closed to European and African continent. In the present paper, a specimen of Seriola dumerili weighing 70 kg and a smaller Seriola fasciata specimen, captured in waters belonging to Selvagens Islands (Madeira Arquipelago), were analyzed. Fishes from this genus were implicated in previous suspected ciguatera poisoning outbreaks in the Portuguese Madeira Arquipelago in the North Atlantic Ocean. Analysis was performed by two approaches, a functional method using cerebellar granule cells and by ultraperformance liquid chromatography-mass spectrometry (UPLC-MS) method. The study was carried out in one portion of the tail muscle of Seriola fasciata and five parts of the body of Seriola dumerili (tail muscle, head, ventral muscle, mid muscle, and liver). The functional method consisted in the modification of the inward sodium current in cerebellar granule cells and the chemical method was a high resolution chromatography, which allowed elucidating the toxin profile in the samples. In addition, UPLC-MS technique was optimized and used for detecting and quantifying CTXs for the first time. After fish extraction and clean up, the chromatograms revealed the presence of CTX-1B at 1111.6 m/z, CTX-3C at 1023.5 m/z, a CTX analogue at 1040.6 m/z, and a CTX from the Caribbean or Indic waters at 1141.6 m/z. Therefore, the results obtained in the present paper for both methods confirm, for the first time, the presence of CTX in fish from Madeira Arquipelago.

Europe has a long tradition of exploiting marine fishes and is promoting marine economic activity through its Blue Growth strategy. This increase in anthropogenic pressure, along with climate change, threatens the biodiversity of fishes and food security. Here, we examine the conservation status of 1,020 species of European marine fishes and identify factors that contribute to their extinction risk. Large fish species (greater than 1.5 m total length) are most at risk; half of these are threatened with extinction, predominantly sharks, rays and sturgeons. This analysis was based on the latest International Union for Conservation of Nature (IUCN) European regional Red List of marine fishes, which was coherent with assessments of the status of fish stocks carried out independently by fisheries management agencies: no species classified by IUCN as threatened were considered sustainable by these agencies. A remarkable geographic divergence in stock status was also evident: in northern Europe, most stocks were not overfished, whereas in the Mediterranean Sea, almost all stocks were overfished. As Europe proceeds with its sustainable Blue Growth agenda, two main issues stand out as needing priority actions in relation to its marine fishes: the conservation of marine fish megafauna and the sustainability of Mediterranean fish stocks.arine fishes exhibit high biodiversity 1,2 and have been culturally and nutritionally important throughout human history 3 . Europe, in particular, has a well-documented history of exploiting marine fish populations, written records of which commence in the classical works of ancient Greece. Although this historical exploitation has undoubtedly altered populations 4,5 and changed many seascapes 6 , marine defaunation in the region has not been as great as in terrestrial systems 7 . However, the use of ocean space and resources is increasing due to Europe's Blue Growth strategy 8 , the nutritional requirements of an expanding human population are growing 9,10 and marine ecosystems will experience unusually rapid changes in future due to climate change 11,12 . Consequently there are imminent threats both to European marine biodiversity and fish resources 13 . It is important, therefore, to assess the threats of extinction to fish species and to ensure consistency in the management approach by the various agencies involved.We analysed data on the conservation status of 1,020 species of Europe's marine fishes from the recent International Union for Conservation of Nature (IUCN) Red List assessments 14 to identify characteristics that make Europe's fishes most susceptible to extinction risk. We then compared the Red List with 115 fish stock assessments (of 31 species) made by intergovernmental agencies charged with providing advice on the exploitation of commercial fishes. Previous comparisons of this sort applied criteria under various modelling assumptions [15][16][17] or limited the comparison to biomass reference points 18 . ResultsOf the 1,020 European marine fish species that were asses...

The growth and reproductive biology of the limpet Patella aspera were studied in the north-eastern Atlantic, Madeira archipelago, to enhance the knowledge concerning biological parameters and population dynamics of this species. This study comprised the estimation of growth rates, sexual maturity, reproduction, recruitment patterns, mortality coefficients and the exploitation rate, and yield-per-recruit (Y/R) based on monthly shell-length frequency data. A total of 16,941 specimens were sampled from January to December 2015. The relative growth pattern exhibited a negative allometric nature of growth for both sexes. The estimated von Bertalanffy growth parameters showed an asymptotic length of 84.15 mm for females and 80.51 mm for males with a growth coefficient of 0.36 and 0.32 year −1 respectively. P. aspera in this geographical area is a moderately long-lived limpet with a predominance of specimens younger than 3 years old. This species is a winter breeder with a reproductive cycle encompassing three main periods namely development, spawning and resting with a synchronous gametogenesis for both sexes. Gonadal development lasts from October to December, spawning likely occurs from January until April and resting occurs from May to September. The mean size at sexual maturity was determined as 41.78 mm for females and 38.29 mm for males and the length at first capture as 42.62 mm. The recruitment pattern was continuous throughout the year with a major peak identified in March. The natural, fishing and total mortalities were similar between sexes, with fishing mortality exerting greatest pressure on this resource. However, yield-per-recruit analysis showed that the stock of P. aspera, in the study area, is exploited at levels below the fishing mortality that returns maximum sustainable yield. This study revealed that currently the stock of P. aspera is under-exploited, nonetheless due to it's slow growth and long life, continuous monitoring and the enforcement of the existing harvest regulations must be accomplished if future overexploitation is to be avoided. Further genetic studies are necessary to establish connectivity of the populations and improve present conservation strategies.

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