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About 19 % of the Italian territory is covered by protected areas (PAs), 5.1 % of which fall in IUCN categories Ia and II, which can be considered strictly protected areas (StPAs). The 2030 EU Biodiversity Strategy sets a target of 30 % coverage for PAs (of which 10 % should be StPAs). We assessed the area coverage of StPAs, for the territory of Italy, with respect to biogeographical regions, ecoregions, elevation range, habitats, and the distribution of species threatened with extinction according to the IUCN Red List (Vulnerable, VU; Endangered, EN; or Critically Endangered, CR). We found that most of the StPAs are located in the Mediterranean biogeographical region, followed by the Alpine and Continental regions, and that the spatial distribution of such protected areas is biased towards higher elevation. Moreover, we found that three of the fourteen terrestrial ecoregions of Italy are not protected at all by StPAs (i.e., Illyrian, Ligurian-Provencal, and Central-Adriatic), while the Po Plain and the Sicilia Sections are only marginally protected. Moreover, nine habitats are not covered by any StPAs including one priority habitat (Inland salt meadows). Finally, we found unprotected species among freshwater fish (21), amphibians (3 VU, 3 CR), reptiles (1 CR), birds (2 NE), mammals (1 VU), and plants (20 VU, 14 EN, 21 CR). Our findings suggest that the current amount and spatial distribution of StPAs of Italy are far from the targets of the EU Biodiversity Strategy and needs improvements. [ABSTRACT FROM AUTHOR]

Macrophyte Biological Index for Rivers (IBMR) has been applied to the superficial waters of Pescara Springs (Popoli, Italy) according to Water Framework Directive 2000/60/EC. Two complementary and not mutually exclusive methodologies were performed to evaluate possible differences in taxa identification and cover estimation: boat survey and interpretation of orthophotos and images taken during SCUBA (Self-Contained Underwater Breathing Apparatus) dive. Data from submerged macrophytes were analyzed by means of exploratory multivariate analysis to detect vegetation associations and their correlation with some abiotic factors (water current velocity, substrate granulometry, detritus type, water depth). Six homogeneous tracts were observed according to hydromorphological characters and to vegetation associations; IBMR and Ecological Quality Ratio (IBMR-EQR) were calculated for each of them. On an average basis, IBMR was 7.84 (trophic status: very high) and IBMR-EQR was 0.63 (quality class: scarce). A good concordance was registered by means of Bland–Altman plot between values obtained by the two methods: 0.57 ± 3.07 (mean ± SD) of percent bias. Nevertheless, IBMR failed to correctly describe the trophic status of the surveyed site, possible due to low dissolved oxygen, high pCO 2 and HCO 3 values. [ABSTRACT FROM AUTHOR]

• Post-fire short-term vegetation dynamics showed a high species turnover. • Alien plant species with c - scores increased over time. • Short-term vegetation recovery involves species-specific strategies such as dispersal ability. • The leaf area did not show any significant pattern over time, with a slight increase observed in the short-term. Wildfire events significantly affect plant communities. Understanding the post-fire vegetation dynamics and how native and alien species interact to shape the composition and structure of the community is crucial to address conservation policy. Dispersal mechanisms and resource exploration strategies are two functional strategies which can explain variability in species response to disturbance. Here, we investigated how functional traits shape the short-term dynamic after a wildfire event in a Mediterranean pine forest. We collected plant co-occurrences and abundances in permanent plots of 100 m2 across four distinct sampling sessions (from late winter to early autumn, every 2 months). Functionally relevant traits including leaf traits and dispersal-related traits were also retrieved for the recorded species. We then derived the Grime's strategies of the recorded species from the collected leaf traits, and we computed the dispersal ability of each species as a function of the corresponding dispersal traits. To compare Grime's strategies and leaf traits across the monitoring cycles, we calculated the community weighted mean for each cycle as the average of species trait values in each plot. Further, we estimated variations in species abundances and species composition within each plot by using temporal turnover analysis, which showed a continuous post-fire increase in community-level vegetation cover and a strong compositional change driven by a spread of alien species. Associating these patterns to the recorded functional traits revealed that dispersal ability is crucial in post-fire recolonization. Moreover, ruderal species, being the most represented strategy soon after the fire, give way over time to more competitive species showing higher leaf area. Thus, short-term vegetation recovery involves different species-specific strategies that shape the ecological succession over time. Our case study highlights that knowledge about how functional traits drive plant colonization strategies is critical to assess the post-fire restoration status of Mediterranean pine forests. [ABSTRACT FROM AUTHOR]