Climate oscillation and alien species invasion influences oceanic
seabird distribution
Peter Carr
Institute of Zoology, Zoological Society of London, Regent’s Park, London, UK , Centre for Ecology and Conservation, University of Exeter, Penryn Campus, Cornwall, UK
Author ProfileJulian Perez-Correa
Institute of Zoology, Zoological Society of London, Regent’s Park, London, UK , Escuela de Ciencias Ambientales, Facultad de Ingeniería, Universidad Espíritu Santo, Samborondón, Ecuador, Imperial College London, London, United Kingdom
Corresponding Author:[email protected]
Author ProfileHeather Koldewey
Conservation and Policy, Zoological Society of London, Regent’s Park, London, UK, Centre for Ecology and Conservation, University of Exeter, Penryn Campus, Cornwall, UK
Author ProfileTom Letessier
Institute of Zoology, Zoological Society of London, Regent’s Park, London, UK , Centre for Marine Futures, Oceans Institute and School of Animal Biology, The University of Western Australia, Crawley, WA, Australia
Author ProfileAbstract
Aim: We aim to document the extent to which climate oscillation and rat
infestation on islands affect the distribution of seabirds at sea.
Location: The Chagos Archipelago, British Indian Ocean Territory,
Central Indian Ocean Methods: At sea observations of seabirds (n = 425)
were collected from 2012 to 2017 during the breeding season. We used
generalized additive models to identify relationships between dominant
seabird families (Laridae, Sulidae, and Procellariidae), geomorphology,
oceanographic variability, and climate oscillation. We built boosted
regression trees to quantify the effects of proximity to both rat-free
and rat-infested islands on seabird distribution, identifying breaking
point thresholds in distribution. Results: We identified oceanic
hotspots and common geomorphic and oceanographic drivers for all seabird
families. We documented positive relationships between Sulidae and
Procellariidae abundance and the Indian Ocean Dipole, as represented by
the Dipole Mode Index. The abundance of Laridae and Sulidae declined
abruptly with greater distance to island. Both families aggregated more
densely (1.08 and 1.25 times higher respectively) and in greater
proximity (distribution thresholds at 16 and 44 km closer to islands,
respectively) next to rat-free island compared with to rat-infested
islands. In contrast, Procellariidae increased in abundance with greater
distance to islands, plateauing at 83 km and were not significantly
influenced by rat presence on nearby islands. We identified areas of
increased abundance at sea under a scenario where rats are eradicated
from infested islands with subsequent seabird recolonization. Main
conclusions: Climate oscillations may cause shifts in seabird
distribution, possibly through changes in regional productivity and prey
distribution. Invasive species eradications and subsequent island
recolonization can lead to predictable distribution gains and increased
competition. Our analysis predicting range extension after successful
eradications enables anticipatory threat-mitigation in these areas,
minimising competition between colonies and thereby maximising the risk
of success and the conservation impact of eradication programmes.