Abstract

The dispersal of many large-seeded plants is thought to have been handicapped by the extinction of megafauna in the late Pleistocene, and due to the ongoing defaunation of the largest of the extant dispersers. Oversized fruits defined as “megafaunal” provide variable amounts of flesh even though many of them cannot be ingested entirely, nor their seeds defecated, by any extant vertebrate. This apparent mismatch lead to the hypothesis of anachronisms involving extinct megafauna as dispersal-mediated selective agents on fruit traits shaped through endozoochory. It has been suggested that free-ranging livestock partially supply the dispersal functions previously provided by those globally or regionally extinct species. However, there is little knowledge on the role of livestock as a surrogate for megafauna dispersal agents relative to living wild dispersers. Here, we focus on seed dispersal of six palm species (Attalea eichleri, Attalea barreirensis, Attalea speciosa, Attalea princeps, Mauritia flexuosa, Acrocomia totai) with large fruits that conform to the so-called “megafaunal syndrome”. Data on seed dispersal were obtained by observations and camera trapping in the Cerrado, Pantanal and Amazonia biomes in Bolivia and Brazil. Rich communities of wild seed dispersers differing among palm species and study areas were recorded, including rodents, monkeys, canids and a wide variety of birds, especially parrots. Long-distance primary dispersal was mainly conducted by parrots, while multiple species acted as short- and medium-distance secondary dispersers. Among livestock, dispersal was limited to seeds of A. totai and A. princeps moved by several species through stomatochory and endozoochory (mainly regurgitation). These results show that the large seeds can be efficiently dispersed externally by a wide array of present-day vertebrates of variable size but much smaller than extinct megafauna and livestock. A knowledge gap of the natural history of these and other plants with oversized fruits assumed to be maladapted for contemporary dispersal may have been partially favoured by neglecting some key disperser guilds (e.g. parrots) and dispersal mechanisms (e.g. ectoozochory). The evaluation of historic and ongoing defaunation of key external dispersers is advocated to understand the influence of actual (rather than putative) dispersers on contemporary frugivore-plant mutualistic interactions.

Highlights

  • Trade-offs between fruit size and seed dispersal ability have been repeatedly highlighted as governing plant-frugivore mutualistic interactions (Wheelwright, 1985; Lord, 2004, Bruun and Poschlod, 2006; Burns, 2013)

  • The number of dispersers varied among palm species; parrots (Psittaciformes) and monkeys (Primates) were recorded as seed dispersers for all of the studied palm species, while other Orders varied in their impact as dispersers of each palm species (Figure 2, Table S2)

  • External dispersers were recorded for A. eichleri, A. barreirensis, and A. speciosa (Figures 2, 4, Table S2)

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Summary

Introduction

Trade-offs between fruit size and seed dispersal ability have been repeatedly highlighted as governing plant-frugivore mutualistic interactions (Wheelwright, 1985; Lord, 2004, Bruun and Poschlod, 2006; Burns, 2013). The megafaunal seed dispersal hypothesis states that some extant plants show “overbuilt” fruits apparently adapted for seed dispersal by very large mammals such as elephant-like gomphotheres and giant ground sloths that went extinct during the Pleistocene in the Neotropics (Janzen and Martin, 1982) These “anachronistic” fruits were assumed to be ecologically ineffective today because of the lack of presentday seed dispersal mechanisms (Janzen and Martin, 1982).This argument implies that the extinction of megafrugivores resulted in marked shifts in the patterns of seed dispersal observed today in extant plants with oversized fruits (Janzen and Martin, 1982; Howe, 1985; Barlow, 2000), with important implications in the ecology, evolution, and conservation of biodiversity. This hypothesis has remained controversial given its vagueness, the discrepancies in its assumptions and the limited or contrary evidence for many of its predictions (Howe, 1985; Hunter, 1989)

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