Abstract
Guadalupe Island, an oceanic island in the northwest of Mexico, is an outlier of the California Floristic Province that has been disturbed by introduced goats for more than a century, with dramatic effects of goats on plant communities and local species extinctions. In 2004 the island went through a successful eradication program. Since then, six previously unrecorded species have been discovered and four supposed extinct species have been found again. Quantifying the true species richness of the island at the time of eradication, to set a benchmark for the future monitoring of this large-scale natural experiment, is both a challenge and a necessity. For this purpose, we estimated (a) current and (b) accumulated historical plant species richness of the island through accumulation functions. Estimation of current species richness was based on the geographical accumulation process of species richness (80 species) obtained from sampling 110 (50 m × 2 m) transects distributed along the island in year 2004. Historical species richness was estimated through the temporal accumulation of species richness (119 species) from botanical records (1,960 specimens reviewed) between 1875 and 2000. The predicted value of historical richness (213 species) is similar to known historical records (218 species), but estimation of current richness (203 species) is significantly higher than accepted extant plant richness (187 species). Our results suggest that currently there may be more plant species living in the island than estimated through recent botanical exploration. Future monitoring of the island as it recovers will clarify this hypothesis.
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Acknowledgements
We are grateful to Luciana Luna and Francisco Casillas for their help in the field work, to Eulogio López for his assistance in checking the herbaria, to Charlotte E. González-Abraham for her work with figures, and to an anonymous reviewer for excellent criticism and advice. We also thank Secretaría de Marina de México and GECI for the facilities during field work. We are especially indebted to the CAS, DS, SD, and UC Herbaria staff for their invaluable help. The financial support that made possible this work was provided by Instituto Nacional de Ecología, México (INE). The second author (EE) thanks the financial support of the Packard Foundation and the Pew Fellowship Program on Marine Conservation.
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Appendix
Appendix
List of the 80 species found during field sampling in Guadalupe Island. Subspecies level is showed, although we used species as the taxonomic unit for our study. Among found species in the field only for Hordeum murinum have been recognized two different subspecies in Guadalupe Island (ssp. murinum and ssp. leporinum). Non-native taxa are marked with an asterisk (*).
Aizoaceae |
*Mesembryanthemum crystallinum |
*Mesembryanthemum nodiflorum |
Amaranthaceae |
Atriplex barclayana |
Aphanisma blitoides |
*Atriplex semibaccata |
*Chenopodium murale |
Apiaceae |
Lomatium insulare |
Arecaceae |
Brahea edulis |
Asteraceae |
Amblyopappus pusillus |
Ambrosia camphorata |
*Centaurea melitensis |
Deinandra greeneana |
*Hypochaeris glabra |
Logfia filaginoides |
Perityle emoryi |
Perityle incana |
*Sonchus oleraceus |
*Sonchus tenerrimus |
Uropappus lindleyi |
Boraginaceae |
*Capsella bursa-pastoris |
Guillenia lasiophylla |
Harpagonella palmeri |
Lepidium oblongum |
Pectocarya linearis ssp. ferocula |
*Plagiobothrys acanthocarpus |
*Plagiobothrys collinus |
*Sisymbrium orientale |
Thysanocarpus erectus |
Cactaceae |
Cylindropuntia prolifera |
Campanulaceae |
Githopsis diffusa |
Triodanis biflora |
Caryophyllaceae |
*Cerastium glomeratum |
*Herniaria hirsuta |
*Silene gallica ssp. capitatum |
Spergularia macrotheca |
Crassulaceae |
Crassula connata |
Cupressaceae |
Callitropsis guadalupensis |
Fabaceae |
Lotus grandiflorus |
Lupinus niveus |
Trifolium microcephalum |
Trifolium palmeri |
Trifolium gracilentum |
Vicia hassei |
Vicia ludoviciana ssp. ludoviciana |
Geraniaceae |
*Erodium cicutarium |
*Erodium brachycarpum |
*Erodium moschatum |
Hydrophyllaceae |
Emmenanthe penduliflora |
Eucrypta chrysanthemifolia |
Phacelia floribunda |
Phacelia phyllomanica |
Malvaceae |
*Malva parviflora |
Sphaeralcea palmeri |
Papaveraceae |
Eschscholzia elegans |
Plantaginaceae |
Plantago ovata |
Poaceae |
*Avena barbata |
*Bromus diandrus |
*Bromus hordeaceus |
*Bromus madritensis ssp. rubens |
*Bromus trinii |
*Hordeum murinum ssp. murinum/ssp. leporinum |
*Lamarckia aurea |
Muhlenbergia microsperma |
Phalaris caroliniana |
*Schismus barbatus |
*Vulpia myuros |
Vulpia octoflora |
Polemoniaceae |
Gilia nevinii |
Leptosiphon pygmaeus ssp. pygmaeus |
Polygonaceae |
Pterostegia drymarioides |
Portulacaceae |
Calandrinia ciliata |
Calandrinia maritima |
Claytonia perfoliata ssp. mexicana |
Resedaceae |
Oligomeris linifolia |
Rosaceae |
Aphanes occidentalis |
Rubiaceae |
*Galium aparine |
Solanaceae |
Lycium californicum |
*Nicotiana glauca |
Themidaeceae |
Dichelostemma capitatum ssp. cinerea |
Urticaceae |
Parietaria hespera |
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Garcillán, P.P., Ezcurra, E. & Vega, E. Guadalupe Island: Lost paradise recovered? Overgrazing impact on extinction in a remote oceanic island as estimated through accumulation functions. Biodivers Conserv 17, 1613–1625 (2008). https://doi.org/10.1007/s10531-008-9370-z
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DOI: https://doi.org/10.1007/s10531-008-9370-z