During the 20th century, Mediterranean landscapes underwent extensive changes. In particular, decreasing grazing pressure combined with abandonment of agricultural uplands favoured the development of Mediterranean forests with a corresponding reduction of open habitats and landscape diversity. In some parts of the Mediterranean basin, including our study area, the reduction of open landscapes took place at the same time as a rapid decline in rabbits as a result of myxomatosis. This study assesses the impact of past changes in landscape and rabbit density on the density and the breeding performance of the eagle owl Bubo bubo, one of the largest predators of Mediterranean ecosystems. Eagle owl density, nest site structure and composition at the landscape level, diet and fecundity of 35 eagle owl nesting territories was analysed for 27 years. The study area is characterized by two distinct areas, the border of the massif and the interior, in which past changes acted differently. Eagle owls in the interior were simultaneously affected by the loss of rabbits, a shift to smaller prey, and by open areas reverting to forest. All of these factors reduced the foraging ef®ciency of the owls. When myxomatosis decimated the rabbit population, owls in the border area switched to other mammals, birds and ®sh, whereas in the interior, alternative prey were less abundant. The main impacts of reduced prey availability and landscape diversity on interior pairs were: (1) lower density of breeding pairs; (2) lower diversity in landscape structure and closer habitats; (3) lower richness and diversity in the diet; (4) later egg-laying dates; (5) lower productivity.

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Yellow‐legged gull Larus michahellis populations have been studied on three archipelagos consisting of 20 islands distributed along 80 km of the French Mediterranean coastline. Population changes were analyzed between 1920 and 2006. In the first decades following their settlement on these islands, the yellow‐legged gull populations showed a continuous exponential growth in the three archipelagos, in agreement with an annual geometric growth rate λ above 1. The population growth ceased to fit this model during the 1980s for the older colonies (Riou and Hyères Islands archipelagos). Thus, we focused on population changes occurring during the period 1982–2000, a pivotal period for which we have both precise census and anthropogenic food resource data, in order to determine environmental factors influencing these population changes using multiple linear regression models. An average annual growth rate of colony size was 1.02 for the last two decades. The changes in landfill availability, the gull density in 1982, and the nesting area in 1982 explained 84.4% of variation in colony size changes between 1982 and 2000. The yellow‐legged gull changes on the islands in the last two decades increased as availability in anthropogenic food resources increased near the colony (positive ΔK). As a consequence, given no reduction in landfill activity or in accessibility for gulls, we expect this region to sustain continuous species expansion in the future.

Summary1. Land snail dispersal abilities are considered poor; however, the current invasion of the French Mediterranean region by Xeropicta derbentina (Krynicki 1836), as well as the past invasions of this region by several other species, seems to contradict this view. 2. Using a multilevel approach, from individual experimentation to landscape analysis, the dispersal abilities and mechanisms allowing the passive dispersal of X. derbentina are studied. 3. The colonization of Provence occurred by stratified diffusion, where short-range active dispersal occurs side by side with long-range passive dispersal. 4. Active dispersal is not as limited as previously thought. In the field, the capturemark-recapture method recorded a maximum distance covered of 42 m in 6 months within a radius of 38 m from the original release point. 5. Temperature and humidity, and therefore the time of year, influence the main type of dispersal. Dispersal is active during wet periods and essentially passive in dry and hot months. 6. Heat avoidance behaviour is one of the mechanisms allowing passive dispersal. 7. Passive dispersal via human activities is the main determinant of X. derbentina distribution within the landscape. In comparison to other species, X. derbentina is found more often in the vicinity of a communication route. 8. These results show that land snails can cover large distances in a lifetime. The potential for active and passive dispersal described in this paper enables X. derbentina to be a successful invasive species and explains the rapid spread and current distribution of this species.

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