Análise de selecção de áreas de caça por uma população de francelho (Faco naumanni) na planície de Évora

Em Portugal, apesar de haver registos históricos da reprodução desta espécie um pouco por todo o país, o francelho (Falco naumanni, Fleischer 1818) desapareceu de quase todo o território nacional estando actualmente restrito à região do Alentejo. Em 2005, 80% da população encontrava-se nas ZPE´s de Castro Verde e Vale do Guadiana (62% e 18% da população nacional, respectivamente (Catry et al. 2005). Ao longo dos últimos anos têm vindo a ser desenvolvidos trabalhos de investigação com o objectivo de conhecer as necessidades ecológicas da espécie nas diferentes colónias, de forma a tentar conciliar a prática de uma agricultura economicamente viável com a conservação de uma espécie que está dependente das práticas agrícolas tradicionais. Os conflitos entre conservação e alteração das práticas agrícolas levam a desafios na gestão deste tipo de habitats. A população de francelho da ZPE Évora, após um período de 12 anos de ausência da espécie como reprodutora na região, tem vindo a aumentar em número de casais reprodutores, desde 1995. A distribuição da espécie na ZPE de Évora, a sua evolução e os principais factores que afectam a sua reprodução foram por nós estudados no ano de 2007. Foi ainda analisada a disponibilidade de habitat de caça para o francelho na área que envolve a principal colónia de Évora de modo a poderem ser sugeridas medidas de gestão adequadas à sua conservação. Concluiu-se que a manutenção de áreas de caça e a conservação dos locais de nidificação existentes e a criação de novos locais passa inevitavelmente pela sensibilização e informação dos proprietários sobre as medidas a aplicar. O recurso a instrumentos de financiamento neste sentido será primordial; ABSTRACT: In Portugal, although there are historical records of the reproduction of this species all over the country, the lesser kestrel (Falco naumanni) disappeared from almost all the national territory being currently restricted to the Alentejo region. In 2005, 80% of the population was in Castro Verde and Vale do Guadiana SPA (62% and 18% of the national population, respectively) (Catry et al. 2005). Over the past few years have been developed research in order to meet the ecological needs of the species in the different colonies, trying to reconcile the practice of an economically viable agriculture and the conservation of a species that is dependent on traditional farming practices. The conflicts between conservation and changing farming practices lead to challenges in managing this type of habitat. The lesser kestrel population of the Évora SPA, after a 12 year absence of the species as breeding in the region, has being increasing in the number of breeding pairs, since 1995. The distribution of the species in the SPA of Évora, its evolution and the main factors affecting their reproduction were studied in 2007. It was also analyzed the availability of hunting habitat for the kestrel in the area surrounding the main colony of Évora so that appropriate management measures can be suggested to their conservation. It was concluded that maintaining hunting areas and conservation of existing nesting sites and the creation of new local inevitably passes through the awareness and information of the owners on the measures to be implemented. The use of financial instruments and the in this direction will be paramount.

Changes in fish assemblage structure after implementation of Marine Protected Areas in the south western coast of Portugal.

Marine Protected Areas (MPAs) are increasingly being recommended as management tools for biodiversity conservation and fisheries. With the purpose of protecting the region's biodiversity and prevent the over exploitation of marine resources, in February 2011 the no-take MPAs of Ilha do Pessegueiro and Cabo Sard~ao were implemented within the “Parque Natural do Sudoeste Alentejano e Costa Vicentina “(PNSACV) Marine Park, south western coast of Portugal. As such, commercial and recreational fishing became prohibited in these areas. In order to evaluate the effects of these no-take MPAs, the structure of their fish assemblages and of adjacent control areas without fishing restrictions were studied between 2011 (immediately after implementation) and 2013 (two years after implementation). A total of 4 sampling campaigns were conducted (summer 2011, winter 2012, summer 2013 and winter 2013) using trammel nets and bottom trawl. Ichthyofaunal assemblages from the no-take MPAs (treatment) were compared with adjacent areas (controls) and changes evaluated as a function of time since protection. Results revealed significant increase in fish abundance after the implementation of the no-take MPAs. Furthermore, significant differences in the structure of fish assemblages (abundance and fish size) between protected and neighbouring areas were rapidly observed upon the implementation of the no-take MPAs. In addition, specimens of larger size occurred more frequently within Ilha do Pessegueiro no-take MPA in the last year of the study. Overall, despite the young age of these no-take MPAs, changes on the structure of their fish assemblages were already evident after only two years of protection, indicating that management measures such as MPA designation may play an important role to promote fisheries sustainable exploitation as well as to protect species with conservation interest.

Alqueva hydro-meteorological experiment(alex): first results of aquatic ecological assessment

The ALqueva hydro-meteorological EXperiment (ALEX) field campaign took place monthly during summer 2014 and consisted in in situ measurements and sampling of water and biological elements, collected from three fixed platforms placed in the lacustrine zone. This integrated overview, including meteorological, environmental and biological results contributes to improve the knowledge of the reservoir dynamics and therefore to propose adequate management measures to preserve the observed biological integrity.

Exploited anadromous fish in Portugal: Suggested direction for conservation and management.

Sea lamprey (Petromyzon marinus) and allis shad (Alosa alosa) have been fished for centuries in mainland Portugal during their upstream spawning migration. Here, biological information is compared for the two species and governance and monitoring data from Portugal are reviewed to propose species-specific courses of future action. Despite a national fisheries legislation common for the two species and the designation of Sites of Community Interest (SCIs) for both, the current conservation needs for sea lamprey and allis shad in Portugal are considered to be distinct. For sea lamprey, conservation priorities must focus on planning fisheries managementinarticulationwithhabitatrecoverytoguaranteecost-effective monitoring andsustainablelong-termexploitationthataddsvaluetolocalcommunitiesandpaysdue taxation. Onthecontrary,conservationconcernsandactionsforallisshadmuststrengthenandbemore proactive in the reduction of fishing mortality, both target (in rivers) and by catch (at sea).There is a need to make better use of the opportunities inherent in the Habitats Directive and the possibility to define specific management actions within SCIs. To this effect, it will be necessary to revise existing legislation and guarantee better articulation between jurisdictional authorities. A good example in this direction is the articulation already established in the river Mondego where habitat restoration, fish monitoring and effective species-specific fisheries control measures have been taken and implemented in recent years by a large institutional partnership.