Aotearoa seabird islands

Islands support some of the greatest numbers of endemic species (Whittaker & Fernández-Palacios 2007) but are highly vulnerable to anthropogenic degradation (Kier et al. 2009). The introduction of invasive, predatory mammals especially has resulted in sharp declines of native island species (Tennyson & Martinson 2006; Banks et al. 2008; Jones et al. 2008; Medina et al. 2011) due to a lack of evolved behavioral capacities of island fauna to deal with predation (Blackburn et al. 2004). Mammal eradication is now a primary conservation tool, with over 700 attempts globally (DIISE 2018). Mammal eradication is assumed to allow islands to naturally return to their pre-invaded condition (e.g. Howald et al. 2007). However, many restored islands differ from their uninvaded counterparts (Jones 2010) in part because innate behaviors (e.g. philopatry) can limit the dispersal of species to restored islands in the first place (Greenwood & Harvey 1982; Koenig et al. 1996). Even when dispersal to restored islands is successful, the process of community reassembly, due to variability in colonization rates and temporal differences in important behavioral interactions between species (Young et al. 2001) may lead to a different community structure from pre-invaded conditions (Choi et al. 2008). This has important implications for holistic restoration of ecosystem function, which is dependent upon recovery of key ecosystem engineers.

Aotearoa is the world’s invasive species eradication pioneer, where conservation practitioners have initiated eradications since the early 1900s, thereby generating a chronosequence of >100 islands in varying stages of recovery (Clout & Russell 2006, Bellingham et al. 2010). Many of Aotearoa’s island communities are dominated by seabirds, an essential ecosystem engineer that facilitates nutrient cycling on islands (Smith et al. 2011). For my dissertation, I explored differences in seabird community assemblages related to island-specific histories of mammal introductions and subsequent eradications, quantified the potential for competition in shaping post-eradication seabird communities, and assessed transferability of species distribution and habitat models to predict seabird responses at inaccessible islands.

Island biogeography disrupted by the lasting effects of mammalian invasions

The theory of island biogeography is a central tenet of ecology, explaining that biological communities are modulated by area and isolation. While island biogeographical principles have been used post hoc to explain distributions of taxa, opportunities to observe biogeographic forcing on faunal community assembly in situ are scarce, as the generation of novel island community assemblages is rare and requires extensive timeframes to study. However, recovery of islands after invasive species eradication offers a unique opportunity to observe biogeographic forcing on community assembly at realistic spatiotemporal scales. Using data from Aotearoa New Zealand, the world's leader in invasive species eradications, my coauthors and I sought to understand the relative role of abiotic (geography) and biotic (invasive species depredation) factors in shaping seabird community assemblages. We amassed one of the largest long-term invasive mammal datasets, documenting seabird breeding presence, invasive species arrival and subsequent eradications, and restoration programs for >500 islands, with observations from 1664 – 2020. We found strong evidence that seabird assemblages are consistent with patterns of island biogeography, but these trends were disrupted by invasive mammals, with legacy effects detectable long after mammal eradication.

Low forage competition between seabird species during passive island recovery

Following invasive mammal eradications, seabirds slowly return to establish breeding colonies during a passive island recovery period. Understanding resource use, particularly as it relates to reproductive output, can help explain individual species recruitment rates and population growth. We monitored five species of sympatrically breeding Procellariiformes on a recovering island in Aotearoa New Zealand by collecting dietary samples and measuring chick growth. Our analysis of diet revealed that adults provision chicks differently than for their own means, with chick diets of lower trophic levels and possibly more lipid-rich. However, we detected little effect of diet on measures of chick growth and survival. Our results suggest quality of forage may not be limiting seabird productivity during passive island recovery.

Vegetative succession and seabird activity during passive island recovery

We examine seabird and vegetative changes at Pokohinu (Burgess) Island, predator-free for almost 30 years, of the Mokohinau Islands. In 2009, we documented seabird distributions, plant diversity, and soil depth across the island and performed smaller surveys in 2014 and 2019. We found an overall 62.5% increase in seabird burrow densities with a strong spatial overlap of species distributions. Diversity of plant species also significantly increased, possibly due to the increased abundance of seed-dispersing birds and the simultaneous expansion of invasive plant species. In addition, we performed burrow and vegetation surveys at other Mokohinau Islands that lack same extent of past human disturbance as Pokohinu, which is a retired lighthouse and farm. Seabird densities between islands were comparable but plant communities lacked many of the invasive species found at Pokohinu. Overall, our results suggest that vegetative cover might not be limiting nesting habitat availability within the Mokohinaus, as seabirds are able to utilize areas dominated by dense vegetation. We emphasize the importance of understanding vegetative succession during recovery periods which may help explain recolonization rates for more specialist species.

References

Banks et al. 2008. Boreal Environ Res 13:3-16
Bellingham et al. 2010 NZ J Ecol 34:115-136
Blackburn et al. 2004 Science 305:1955-1958
Choi et al. 2008 Ecoscience 15:53-64
Clout & Russell 2006 in Assessment and Control of Biological Invasion Risks (eds F. Koike et al.)
DIISE 2015 http://diise.islandconservation.org
Greenwood & Harvey 1982 Annu Rev Ecol Syst 13:1-21
Howald et al. 2007 Conserv Biol 21:1258-1268
Jones 2010 Ecol Appl 20:1204-1216
Jones et al. 2008 Conserv Biol 22:16-26
Kier et al. 2009 PNAS 106:9322-9327
Koenig et al. 1996 Trends Ecol Evol 11:514-517
Medina et al. 2011 Global Change Biol 17:3503-3510
Smith et al. in Seabird Islands: Ecology, Invasion, and Restoration (eds C. P. H. Mulder et al.)
Tennyson & Martinson 2006 Extinct Birds of New Zealand
Whittaker & Fernández-Palacios 2007 Island Biogeography: Ecology, Evolution, and Conservation