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dc.contributor.authorLauzon-Guay, Jean-Sebastienen_US
dc.contributor.authorScheibling, Robert Ericen_US
dc.contributor.authorBarbeau, Myriam A.en_US
dc.date.accessioned2013-07-04T18:44:25Z
dc.date.available2013-07-04T18:44:25Z
dc.date.issued2008-03en_US
dc.identifier.citationLauzon-Guay, Jean-Sebastien, Robert E. Scheibling, and Myriam A. Barbeau. 2008. "Modelling phase shifts in a rocky subtidal ecosystem." Marine Ecology Progress Series 375: 25-39. doi:10.3354/meps07758en_US
dc.identifier.issn0171-8630en_US
dc.identifier.urihttp://hdl.handle.net/10222/29659
dc.identifier.urihttp://dx.doi.org/10.3354/meps07758
dc.description.abstractThe rocky subtidal ecosystem of the Atlantic coast of Nova Scotia is characterised by 2 community states, kelp beds and urchin barrens that alternate on a decadal time scale. While the shift from barrens to a kelp bed requires a large perturbation, namely a disease outbreak causing urchin mass mortality, the reverse shift is more gradual and mediated by the formation and propagation of destructive grazing aggregations (or fronts) of sea urchins Strongylocentrotus droebachiensis. We have developed a spatial model for the re-establishment of kelp beds and the formation of a feeding front of urchins in order to describe transitions (phase shifts) between kelp bed and barrens states following an urchin mass mortality event. Our model includes size-specific movement, growth, and survival of urchins, as well as growth of kelp and grazing by urchins. The position of the kelp bed-barrens interface (or grazing front) predicted by our model is in general agreement with field observations at 2 sites and for up to 7 yr after a mass mortality event. Elasticity analysis showed that daily foraging movements by individual urchins have the greatest effect on the position of the feeding front and the density of the urchins there. Survival and recruitment rates of urchins also have large effects on urchin density at the front. The density of urchin populations in deep-water thermal refuges (from a disease agent) and the distance between these source populations and remnant or emergent kelp beds have large effects on the time required for the re-formation of a feeding front after an event of urchin mass mortality. These findings suggest that site-specific characteristics should be taken into account in the development of sustainable harvesting strategies and habitat-based management of the urchin fishery.en_US
dc.language.isoenen_US
dc.publisherInter-Research, Nordbuente 23 Oldendorf/Luhe 21385 Germany, [mailto:ir@int-res.com], [URL:http://www.int-res.com/]en_US
dc.relation.ispartofMarine Ecology Progress Seriesen_US
dc.subjectSea urchinsen_US
dc.subjectSustainable developmenten_US
dc.subjectBenthic environmenten_US
dc.subjectKelpsen_US
dc.subjectFishery managementen_US
dc.subjectGrazingen_US
dc.subjectRecruitmenten_US
dc.subjectOutbreaksen_US
dc.subjectCoastal zoneen_US
dc.subjectHarvestingen_US
dc.subjectEchinoideaen_US
dc.subjectSurvivalen_US
dc.subjectStrongylocentrotus droebachiensisen_US
dc.subjectMarine invertebratesen_US
dc.subjectModelsen_US
dc.subjectKelp bedsen_US
dc.subjectFisheriesen_US
dc.subjectCoastsen_US
dc.subjectGrowth rateen_US
dc.subjectMarineen_US
dc.subjectFeedingen_US
dc.subjectMortalityen_US
dc.subjectForaging behaviouren_US
dc.subjectPhase shiften_US
dc.titleModelling phase shifts in a rocky subtidal ecosystemen_US
dc.typearticleen_US
dc.identifier.volume375en_US
dc.identifier.startpage25en_US
dc.rights.holderCopyright © 2009 Inter-Research
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