Aim: Species are responding to climate change by changing their distributions, creating debate about the effectiveness of existing networks of protected areas. As a contribution to this debate, we assess whether regional winter abundances and distribution of the SmewMergellus albellus, a migratory waterbird species listed on Annex I (EUBirds Directive) that overwinters exclusively in European wetlands, changed during 1990–2011, the role of global warming in driving distributional changes and the effectiveness of the network of Special Protection Areas (SPAs,EUBirds Directive) in the context of climate change.Location: Europe.Methods: We used site‐specific counts (6,883 sites) from 16 countries covering the entire flyway to estimate annual abundance indices and trends at country, region (north‐eastern, central and south‐western) and flyway scales, inside and outsideSPAs. We fitted autoregressive models to assess the effect of winter temperature on the annual abundance indices whilst accounting for autocorrelation.Results: The Smew wintering distribution shifted north‐eastwards in Europe in accordance with the predictions of global warming, with increasing numbers in the north‐eastern region and declines in the central region. Trends in wintering numbers were more positive inSPAs on the north‐eastern and south‐western part of the flyway. However, a large proportion of the wintering population remains unprotected in north‐eastern areas outside of the existingSPAnetwork.Main conclusions: SPAs accommodated climate‐driven abundance changes in the north‐eastern region of the wintering distribution by supporting increasing numbers of Smew in traditional and newly colonized areas. However, we highlight gaps in the current network, suggesting that urgent policy responses are needed. Given rapid changes in species distributions, we urge regular national and international assessments of the adequacy of theEUNatura 2000 network to ensure coherence in site‐safeguard networks for this and other species.

Analysis of coordinated Greater Scaup (Aythya marila) count data from the last 30 years showed a 38.1% decrease in wintering numbers in North-West Europe, from 309,000 during 1988–1991 to c.192,300 individuals during 2015–2018. Annual trends in wintering numbers differed throughout the range. Numbers decreased in the UK, Ireland, and in the Netherlands, while numbers were stable in Denmark. Germany, Poland, Sweden, and Estonia showed increasing numbers, suggesting a shift in the distribution of the species within its wintering grounds towards the east and north. Higher temperatures in northern and eastern areas were correlated with the range shift of the wintering distribution. Deaths from bycatch drowning of Scaup in fishing gear have significantly decreased in recent decades in the Netherlands, where currently the greatest threat is considered the deterioration of food resources. The increasing concentration of wintering Scaup in coastal Poland and Germany (where lack of effective implementation of conservation measures fail to protect the species from the impacts of bycatch and declining food quality) pose major threats to the entire population.

We used ancient DNA techniques to amplify mitochondrial DNA fragments [cytochrome b (cyt b) and control region (CR)] from four museum specimens that represent, to our knowledge, the last testimony of the introduction of – now extinct – mongooses in Italy. We assessed the identity, origin and genetic variability of Italian mongooses using a species‐level assignation Bayesian approach and haplotype network analysis. The genetic diversity (cyt b and CR) among Italian individuals was null. The cyt b sequences from the four museum specimens clearly established the Indian grey mongoose Herpestes edwardsii as the species having been introduced in Italy in the mid‐XXth century. The latter had at least been released twice within a period of 10 years (Circeo NP and Capalbio, c. 200 km northward), probably from the same captive stock of the Giardino Zoologico di Roma. Assessment of genetic variability and haplotype network including native representatives of H. edwardsii suggested that the introduced pool likely originated from Pakistan or India. It appears that a combination of deleterious factors including low genetic diversity, restricted range and nonadaptation to western Palaearctic winter conditions is responsible for the extinction of the species in Italy. However, the lack of knowledge on the life‐history traits and population dynamics of H. edwardsii prevents from further discussion of the factors that likely promoted its extinction process.