Abstract

Farming impacts animal-mediated seed dispersal through mechanisms operating on at least two spatial scales. First, at the landscape scale, through habitat loss and land conversion to agriculture/livestock grazing, and second, at the farm scale, via a local intensification of agricultural practices. These two scales of farming impact seed dispersal function but have rarely been integrated. In particular, studies evaluating the effect of agriculture on the seed dispersal function of frugivorous birds in Mediterranean ecosystems are lacking. This study evaluates the role of landscape transformation, from fruit-rich woodland habitats to olive grove landscapes, together with local intensive practices of soil management on the persistence of the seed dispersal function for Mediterranean fleshy-fruited plants in olive landscapes of south Spain. We used bird censuses, mist-nets, and seed traps to characterize avian frugivore assemblages, frugivory, and seed deposition in the seminatural woodland habitat (SNWH) patches and olive fields of 40 olives farms spanning 20 localities distributed across the whole range of olive cultivation in Andalusia (southern Spain). We found that despite the remarkable dispersal function of olive grove landscapes, avian frugivore abundance and diversity, frugivory, and seed arrival decreased in olive fields compared to SNWH patches. Likewise, SNWH cover loss and/or olive growing expansion decreased avian frugivory and seed arrival. Interestingly, the habitat effects in the olive farms often depended on the landscape context. In particular, less diverse fruit-eating bird assemblages pooled in SNWH patches as olive grove cover increased or SNWH decreased in the landscape, while remaining relatively invariant in the olive fields. Finally, compared to conventional intensive agriculture, low-intensity management increased frugivory and seed deposition. We conclude that olive fields are less permeable to frugivores than expected due to the agroforest-like nature of these landscapes and that the presence of SNWH patches is crucial for the maintenance of frugivory and seed dispersal in agricultural landscapes. These results evidence that woodland habitat loss by olive expansion and intensive practices seriously threaten the dispersal service in olive-dominated landscapes. Maintenance, restoration, and promotion of woodland patches should be prioritized for the conservation of seed dispersal service and for enhancing the functional connectivity in human-shaped olive landscapes.

Highlights

  • Seed dispersal by frugivores is an important ecosystem service that promotes spontaneous natural regeneration of vegetation and contributes to shaping natural plant communities and their dynamics in many regions (Herrera, 1985; Lázaro et al, 2005; Tomback, 2016)

  • The seed dispersal of woody plants by frugivorous vertebrates is a major driver of the dynamics of tropical forests and Mediterranean woodlands (e.g., Herrera, 1995; Muller-Landau and Hardesty, 2005) where frugivores act as mobile links for connecting plant populations across landscape patches (Henry et al, 2007; Pérez-Méndez et al, 2017; Parejo-Farnés et al, 2020)

  • We found an interdependent effect of H x OGC, meaning that frugivores increased their abundance in seminatural woodland patches but remained invariant in the olive field as olive grove cover increased in the landscape (Figure 2A)

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Summary

Introduction

Seed dispersal by frugivores is an important ecosystem service that promotes spontaneous natural regeneration of vegetation and contributes to shaping natural plant communities and their dynamics in many regions (Herrera, 1985; Lázaro et al, 2005; Tomback, 2016). At the landscape scale, land conversion to agriculture and/or livestock grazing provokes the direct loss of natural habitats, decreasing the population sizes of frugivores and fleshy-fruited plants, and increasing isolation among remnant habitat patches, This causes plant metapopulations to collapse as it restricts animal mobility and alters seed deposition patterns. Reduced levels of frugivory at these two scales are expected as fruit-bearing plants become scarce in the landscape and in the areas dedicated to crop yield Some of these effects have been described in both temperate and tropical systems (e.g., Lozada et al, 2007; Pejchar et al, 2008; Martínez and García, 2017), they have not been considered together (in an integrative way), which would provide a comprehensive view of the impact of farming on the persistence of animal-mediated seed dispersal. Considering the operating mechanisms at these two scales together enables us to directly associate patterns of seed dispersal decay with specific human actions (expansion of croplands, destruction or substantial modification of habitat features, intensification of agricultural practices), which allows researchers to formulate appropriate corrective measures

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