Seabird Group Seabird Group

The fate of rescued Manx Shearwaters following grounding

Martyna Syposz1,2* ORCID logo and Oliver Padget1 ORCID logo

https://doi.org/10.61350/sbj.35.7

1 Department of Biology, Biology Research and Administration Building, University of Oxford, 11a Mansfiield Road, Oxford, UK, OX1 3SZ.

2 Department of Biology, University of Gdansk, Poland.

Full paper

Abstract

Manx Shearwaters Puffinus puffinus, like other procellariiform seabirds, spend most of their lives at sea and are encountered on land only when breeding at colonies or if they are grounded due to unfavourable weather conditions or exposure to artificial light. Here, we used historical ringing data to explore the age class structure and spatial patterns of Manx Shearwater groundings and examined ringing and recovery data to identify records of post-grounding survival for first-year and adult birds. We noted 35 cases, out of 6,381 ringed grounded shearwaters, where a bird went on to be recaptured, including two individuals that were later recorded as having successful breeding attempts. While this constitutes only a small number of birds confirmed to have survived following grounding, it is likely to be a considerable underestimate of survival considering the low probability of recapturing a surviving shearwater. Finally, we found that a greater proportion of grounded birds were first-years compared to adult shearwaters, and that adults were found to be grounded further away from colonies than first-year birds. This may be indicative of differential impacts of light pollution at different life stages.

Introduction

Procellariiform seabirds are one of the most threatened groups of birds. Major threats include invasive species, bycatch in fisheries, hunting and climate change (Dias et al. 2019). They spend most of their life at sea and, under normal circumstances, come to land only to breed at colonies located around coastlines or on offshore or oceanic islands (Warham 1990). Procellariiformes are, however, sometimes encountered on land away from their colonies after grounding, perhaps in association with light pollution, oil spills or unfavourable weather conditions such as storms (Telfer et al. 1987; Camphuysen et al. 1999, 2002; Rodríguez et al. 2017a). These ‘groundings’ peak shortly after the fledging period, when mostly juvenile shearwaters can become stranded in artificially lit towns, cities, ships and oil platforms near their nesting sites (Rodríguez et al. 2017a). In response, conservation organisations and local volunteers may deploy personnel to rescue, ring and release grounded shearwaters close to large colonies (e.g. Le Corre et al. 2002; Day et al. 2003; Rodríguez et al. 2017b).

Efforts have been made to monitor the body condition of grounded seabirds (Rodríguez et al. 2017b; Cuesta-García et al. 2022), as higher weight is an indication of higher probability of survival for juvenile seabirds (Perrins et al. 1973; Becker & Bradley 2007; Maness & Anderson 2013). For example, a study comparing the weight of juvenile Short-tailed Shearwaters Puffinus tenuirostris recovered at different locations indicated that birds grounded due to light pollution had lower body weights compared to near-fledging birds at the colony, while water-logged fledglings found washed up on beaches were in the poorest condition of the three groups (Rodríguez et al. 2017b). Whilst considerable effort is put into understanding the consequences of seabird grounding, little is known about survival to breeding age of rescued fledglings, which is important for estimating the impact of grounding casualties on seabird populations (Simons 1984; Fontaine et al. 2011; Griesemer & Holmes 2011; Gineste et al. 2017).

Our study species, the Manx Shearwater P. puffinus, breeds mainly on three islands in Great Britain (Fig. 1A). While the species’ total population is estimated at 1.03–1.18 million individuals (Birdlife International 2015), a combination of hard-to-access breeding areas as well as nests located in burrow chambers, makes it difficult to accurately estimate the population size or its trend (Perrins et al. 2018). Like other procellariiform seabirds, Manx Shearwaters are affected by light pollution and unfavourable weather conditions, with grounding being reported mainly near colonies (Rodríguez et al. 2008; Miles et al. 2010; Syposz et al. 2018). Existing studies of grounding impacts, however, have mainly focused on a single location, failing to report the events at a larger scale.

Here, using ringing and recovery data, we investigated the age class structure and spatial distribution of Manx Shearwater groundings around Britain and Ireland, as well as records of confirmed survival of individuals following rescue. Adult Procellariiformes are thought to be less susceptible than juveniles to grounding caused by light pollution (Camphuysen et al. 1999; Troy et al. 2013; Rodríguez et al. 2015; Syposz et al. 2018), thus we expected to find differences in the frequency and distribution of grounding events depending on age class. Furthermore, survival rates of adult procellariform seabirds are higher than those of fledging juveniles (Perrins et al. 1973; Simons 1984; Jenouvrier et al. 2008), thus we expected that the probability of recapture after an initial grounding event would be higher in adults than juveniles.

Acknowledgements

We thank the BTO Ringing Scheme for providing data from historically ringed and re-trapped Manx Shearwaters. The BTO Ringing Scheme is funded by a partnership of the British Trust for Ornithology, the Joint Nature Conservation Committee (on behalf of Natural England, Natural Resources Wales, NatureScot and the Department of Agriculture, Environment & Rural Affairs, (Northern Ireland)), the National Parks and Wildlife Service (Ireland) and the ringers themselves. We would like to also thank The Wildlife Trust of South and West Wales, Bardsey Bird Observatory, Copeland Bird Observatory and Edward Grey Institute (EGI). Special thanks go to Steve Sutcliff and John Hayes for rescuing birds from the refinery, as well as other volunteers and ringers that contributed to the rescue efforts. We also thank Skokholm Bird Observatory for providing data on re-trapped birds and Prof. Tim Guilford, Dr Natasha Gillies and two anonymous referees for useful feedback on this manuscript. OP was supported by a Junior Research Fellowship at St John’s College, Oxford.

References

Ainley, D. G., Podolsky, R., Deforest, L., & Spencer, G. 2001. The Status and Population Trends of the Newell’s Shearwater on Kaua’i: Insights from Modeling. Studies in Avian Biology 22: 108–123.

Becker, P. H., & Bradley, S. J. 2007. The role of intrinsic factors for the recruitment process in long-lived birds. Journal of Ornithology 148: 377–384. [Crossref]

Birdlife International. 2015. European Red List of Birds. European Red List of Birds. Office for Official Publications of the European Communities, Luxembourg.

Brooke, M. 1990. The Manx Shearwater. Poyser, London.

Camphuysen, C. J., Heubeck, M., Cox, S. L., Bao, R., Humple, D., Abraham, C., & Sandoval, A. 2002. The Prestige oil spill in Spain. Atlantic Seabirds 4: 131–140.

Camphuysen, C. J., Wright, P. J., Leopold, M., Hüppop, O., & Reid, J. B. 1999. A review of the causes, and consequences at the population level, of mass mortalities of seabirds. ICES Cooperative Research Report 232: 1–66.

Le Corre, M., Ollivier, A., Ribes, S., & Jouventin, P. 2002. Light-induced mortality of petrels: A 4-year study from Réunion Island (Indian Ocean). Biological Conservation 105: 93–102. [Crossref]

Cuesta-García, M., Rodríguez, A., Martins, A. M., Neves, V., Magalhães, M., Atchoi, E., Fraga, H., Medeiros, V., Laranjo, M., Rodríguez, Y., Jones, K., & Bried, J. 2022. Targeting efforts in rescue programmes mitigating light-induced seabird mortality: First the fat, then the skinny. Journal for Nature Conservation 65: 126080. [Crossref]

Day, R. H., Cooper, B. A., & Telfer, T. C. 2003. Decline of Townsend’s (Newell’s) Shearwaters (Puffinus Auricularis Newelli) on Kauai, Hawaii. The Auk 120: 669–679. [Crossref]

Dias, M. P., Martin, R., Pearmain, E. J., Burfield, I. J., Small, C., Phillips, R. A., Yates, O., Lascelles, B., Borboroglu, P. G., & Croxall, J. P. 2019. Threats to seabirds: A global assessment. Biological Conservation 237: 525–537. [Crossref]

Fontaine, R., Gimenez, O., & Bried, J. 2011. The impact of introduced predators, light-induced mortality of fledglings and poaching on the dynamics of the Cory’s shearwater (Calonectris diomedea) population from the Azores, northeastern subtropical Atlantic. Biological Conservation 144: 1998–2011. [Crossref]

Gineste, B., Souquet, M., Couzi, F. X., Giloux, Y., Philippe, J. S., Hoarau, C., Tourmetz, J., Potin, G., & Le Corre, M. 2017. Tropical Shearwater population stability at Reunion Island, despite light pollution. Journal of Ornithology 158: 385–394. [Crossref]

Griesemer, A. M., & Holmes, N. D. 2011. Newell’s shearwater population modeling for Habitat Conservation Plan and Recovery Planning. Technical Report No. 176. The Hawai`i-Pacific Islands Cooperative Ecosystem Studies Unit & Pacific Cooperative Studies Unit, University of Hawai`i, Honolulu, Hawai’i.: 68.

Jenouvrier, S., Tavecchia, G., Thibault, J. C., Choquet, R., & Bretagnolle, V. 2008. Recruitment processes in long-lived species with delayed maturity: Estimating key demographic parameters. Oikos 117: 620–628. [Crossref]

Maness, T. J., & Anderson, D. J. 2013. Predictors of juvenile survival in birds. Ornithological Monographs 78: 1–55. [Crossref]

Miles, W., Money, S., Luxmoore, R., & Furness, R. W. 2010. Effects of artificial lights and moonlight on petrels at St Kilda. Bird Study 57: 244–251. [Crossref]

Otis, D. L., Burnham, K. P., White, G. C., & Anderson, D. R. 1978. Statistical Inference from Capture Data on Closed Animal Populations. Wildlife Monographs 62: 3–135.

Perrins, C., Harris, M. P., & Britton, C. K. 1973. Survival of Manx Shearwaters Puffinus Puffinus. Ibis 115: 535–548. [Crossref]

Perrins, C., Padget, O., Connell, M. O., Brown, R., Eagle, G., Roden, J., Stubbings, E., & Wood, M. J. 2018. A census of breeding Manx Shearwaters Puffinus puffinus on the Pembrokeshire Islands of Skomer, Skokholm and Midland in 2018. Seabird 32: 106–118. [Crossref]

Rodríguez, A., Arcos, J. M., Bretagnolle, V., Dias, M. P., Holmes, N. D., Louzao, M., Provencher, J., Raine, A. F., Ramírez, F., Rodríguez, B., Ronconi, R. A., Taylor, R. S., Bonnaud, E., Borrelle, S. B., Cortés, V., Descamps, S., Friesen, V. L., Genovart, M., Hedd, A., Hodum, P., Humphries, G. R. W., Le Corre, M., Lebarbenchon, C., Martin, R., Melvin, E. F., Montevecchi, W. A., Pinet, P., Pollet, I. L., Ramos, R., Russell, J. C., Ryan, P. G., Sanz-Aguilar, A., Spatz, D. R., Travers, M., Votier, S. C., Wanless, R. M., Woehler, E., & Chiaradia, A. 2019. Future directions in conservation research on petrels and shearwaters. Frontiers in Marine Science 6: 94. [Crossref]

Rodríguez, A., Holmes, N. D., Ryan, P. G., Wilson, K. J., Faulquier, L., Murillo, Y., Raine, A. F., Penniman, J. F., Neves, V., Rodríguez, B., Negro, J. J., Chiaradia, A., Dann, P., Anderson, T., Metzger, B., Shirai, M., Deppe, L., Wheeler, J., Hodum, P., Gouveia, C., Carmo, V., Carreira, G. P., Delgado-Alburqueque, L., Guerra-Correa, C., Couzi, F. X., Travers, M., & Corre, M. Le. 2017a. Seabird mortality induced by land-based artificial lights. Conservation Biology 31: 986– 1001. [Crossref]

Rodríguez, A., Moffett, J., Revoltós, A., Wasiak, P., McIntosh, R. R., Sutherland, D. R., Renwick, L., Dann, P., & Chiaradia, A. 2017b. Light pollution and seabird fledglings: Targeting efforts in rescue programs. Journal of Wildlife Management 81: 734–741. [Crossref]

Rodríguez, A., & Rodríguez, B. 2009. Attraction of petrels to artificial lights in the Canary Islands: Effects of the moon phase and age class. Ibis 151: 299–310. [Crossref]

Rodríguez, A., Rodríguez, B., Barone, R., Pérez, B., & Hernández, A. 2008. Status and conservation requirements of Manx shearwaters Puffinus puffinus on Tenerife (Canary Islands). Alauda 76: 72–74.

Rodríguez, A., Rodríguez, B., & Negro, J. J. 2015. GPS tracking for mapping seabird mortality induced by light pollution. Scientific Reports 5: 1–11. [Crossref]

Sharp, B. E. 2008. Post-release survival of oiled, cleaned seabirds in North America. Ibis 138: 222–228. [Crossref]

Simons, T. R. 1984. A Population Model of the Endangered Hawaiian Dark-Rumped Petrel. The Journal of Wildlife Management 48: 1065–1076. [Crossref]

Syposz, M., Gonçalves, F., Carty, M., Hoppitt, W., & Manco, F. 2018. Factors influencing Manx Shearwater grounding on the west coast of Scotland. Ibis 160: 846–854. [Crossref]

Telfer, T. C., Sincock, J. L., Byrd, G. V., & Reed, J. R. 1987. Attraction of Hawaiian seabirds to lights, conservation efforts and effects of moon phase. Wildlife Society Bulletin 15: 406–413.

Troy, J. R., Holmes, N., Veech, J., & Green, M. 2013. Using observed seabird fallout records to infer patterns of attraction to artificial light. Endangered Species Research 22: 225–234. [Crossref]

Warham, J. 1990. The Petrels: Their Ecology and Breeding Systems. Academic Press, London.

Wynn, J., Padget, O., Mouritsen, H., Perrins, C., & Guilford, T. 2020. Natal imprinting to the Earth’s magnetic field in a pelagic seabird. Current Biology 30: 2869-2873.e2. [Crossref]