2014
DOI: 10.1642/auk-13-243.1
|View full text |Cite
|
Sign up to set email alerts
|

Resource partitioning in three congeneric sympatrically breeding seabirds: Foraging areas and prey utilization

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
2
1
1
1

Citation Types

1
38
1

Year Published

2016
2016
2024
2024

Publication Types

Select...
8

Relationship

1
7

Authors

Journals

citations
Cited by 42 publications
(40 citation statements)
references
References 42 publications
1
38
1
Order By: Relevance
“…Such ecologically similar species are likely to have to partition resources to coexist (Schoener 1974, Jonsson et al 2008, Robertson et al 2014. Such ecologically similar species are likely to have to partition resources to coexist (Schoener 1974, Jonsson et al 2008, Robertson et al 2014.…”
Section: Our Results Demonstrated a Clear Split In Collaredmentioning
confidence: 99%
“…Such ecologically similar species are likely to have to partition resources to coexist (Schoener 1974, Jonsson et al 2008, Robertson et al 2014. Such ecologically similar species are likely to have to partition resources to coexist (Schoener 1974, Jonsson et al 2008, Robertson et al 2014.…”
Section: Our Results Demonstrated a Clear Split In Collaredmentioning
confidence: 99%
“…Sandeels are high energy prey for seabirds (Rindorf, Wanless, & Harris, ; Wanless, Harris, Redman, & Speakman, ), and Shetland lacks suitable alternatives (Furness & Tasker, ). Juvenile age classes (0‐ and 1‐group) are especially important because their smaller size, greater abundance and availability within surface waters than older sandeels gives access to a wider range of seabirds (Rindorf et al., ; Robertson et al., ). Recent sandeel scarcity around Shetland is attributed to low recruitment in most years since the mid‐1980s, linked to hydroclimatic changes affecting hatching dates, survival and transport of larvae from major spawning areas north/west of Orkney (Poloczanska, Cook, Ruxton, & Wright, ; Wright & Bailey, ).…”
Section: Discussionmentioning
confidence: 99%
“…Specifically, we aim to (a) model population and productivity trends for Arctic skua, great skua and their hosts since the 1990s; (b) test for differences in Arctic skua trends according to local great skua and host densities; (c) determine whether variation in breeding success is driving Arctic skua population trends; (d) quantify effects of host productivity (an index of food availability) and great skua density (predation pressure) on Arctic skua breeding success. If bottom‐up pressures are driving Arctic skua declines, we predict steeper declines at colonies where host productivity is lowest, which is most likely where Arctic skuas are dependent entirely on terns for food, as these hosts are highly sensitive to localised food availability (Robertson et al., ). Large colonies of cliff‐nesting hosts such as auks, whose diving ability, flexible time budgets and greater foraging ranges make them less vulnerable than ground‐nesting terns to local food shortage, may buffer availability of food to Arctic skuas in years when terns fail to breed successfully (Furness & Tasker, ).…”
Section: Introductionmentioning
confidence: 93%
“…Terns have a high level of variability in foraging modes (Eglington et al 2014) both within and across years, and appear to rely on trophic level segregation rather than spatial segregation to avoid competition (Robertson et al 2014). This is likely to reflect the foraging behaviour of these groups, which are restricted to smaller home ranges due to their high flight costs, in contrast with pelagic species.…”
Section: Comparison Of Foraging Radius Distributions With Aerial Survmentioning
confidence: 99%
“…In contrast biologging studies provide detailed information on the fine-scale distribution of seabirds, usually during the breeding season (Wakefield et al 2013, Dean et al 2015, Soanes et al 2016, and on broader scale movements during the nonbreeding season (Frederiksen et al 2012, Jessopp et al 2013, Grecian et al 2016. Furthermore, foraging areas can vary annually depending on environmental fluctuations (Robertson et al 2014), a factor that is predicted to increase with climate change (Grémillet andBoulinier 2009, Daunt andMitchell 2013). The temporal scale of tracking is also usually heavily restricted by resources (Wakefield et al 2009).…”
Section: Introductionmentioning
confidence: 99%