Abstract

1. Mechanisms of grass‐ and forb‐seed input and output in the central Monte desert of Argentina were studied in 1995 to test the hypothesis that seed consumption by autumn–winter granivores, especially birds, has qualitative as well as quantitative effects on soil‐seed reserves. 2. The abundance of perennial grass seeds in late summer soils (≈ 2400 seeds m–2 or 0·36 g m–2) remained unchanged the following early spring (≈ 2700 seeds m–2 or 0·39 g m–2), despite the incorporation of about 3000 seeds m–2 or 0·71 g m–2 newly produced grass seeds during autumn–winter. Grass seeds appeared to be heavily consumed, especially the medium‐sized ones. 3. The annual forb‐seed bank was about the same size in late summer (≈ 5500 seeds m–2 or 1·34 g m–2) as in early spring (≈ 6500 seeds m–2 or 1·53 g m–2). Since forb‐seed production had been relatively low (≈ 400 seeds m–2 or 0·12 g m–2), these seeds apparently suffered negligible postdispersal losses. 4. This pattern of grass‐ and forb‐seed loss coincides with the pattern of seed consumption by granivorous birds – on average, 93% of seed mass in bird stomachs was from grass seeds, while only 7% was from forb seeds. 5. Further evidence of a major impact of bird foraging on seed reserves is that the mass of particular grass seeds that was lost from soils was positively correlated with the mass of such seeds in bird diets, and that the main target of bird consumption, i.e. medium‐sized grass seeds, suffered the highest postdispersal loss. 6. It is concluded that autumn–winter granivores in the central Monte desert, particularly birds, mainly consume newly produced grass seeds and that they might have major qualitative as well as quantitative impacts on soil‐seed reserves.

Highlights

  • Seeds and granivores are conspicuous components of arid ecosystems

  • This pattern of grass- and forb-seed loss coincides with the pattern of seed consumption by granivorous birds – on average, 93% of seed mass in bird stomachs was from grass seeds, while only 7% was from forb seeds

  • 0·36 g m–2 of grass seeds in the summer SB and 0·39 g m–2 in the spring SB (ANOVA, F = 0·11, P > 0·70, df = 1166) was estimated, in spite of the 0·71 g m–2 that had entered in autumn–winter (Table 1)

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Summary

Introduction

Seeds and granivores are conspicuous components of arid ecosystems. Though little is known about the fates of seeds once they land on the ground (Chambers & MacMahon 1994), there is convincing evidence of the impact that rodents, ants and fungi have on soil-seed reserves in several North American deserts (Reichman 1979; Brown et al 1986; Crist & MacMahon 1992; Crist & Friese 1993; Price & Joyner 1997).Mares & Rosenzweig (1978) experimentally assessed seed removal rates from ‘seed dishes’ in northern Monte and Sonoran deserts. A major failing of the ‘seed dish’ technique (Mares & Rosenzweig 1978; Parmenter, MacMahon & Vander Wall 1984; Kerley 1991; Morton 1985) is the fact that birds might not remove seeds from trays left out for short periods (but see Vásquez, Bustamante & Simonetti 1995; Lopez de Casenave, Cueto & Marone 1998). In spite of this methodological warning, birds have been often considered unimportant granivores in desert ecosystems In spite of this methodological warning, birds have been often considered unimportant granivores in desert ecosystems (e.g. Heatwole & Muir 1982; Abramsky 1983; Mull & MacMahon 1996; but see Parmenter et al 1984; Thompson, Brown & Spencer 1991; Guo et al 1995)

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