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abstracts of oral and poster presentations - Pacific Seabird Group

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fledglings/pair) was higher than in 2003 (0.35 fledglings/pair). <strong>Pacific</strong> saury (Cololabis saira) <strong>and</strong> <strong>Pacific</strong> s<strong>and</strong><br />

lance (Ammodytes hexapterus) dominated 2003 diets, whereas rockfish (Sebastes spp.), s<strong>and</strong> lance, <strong>and</strong> salmon<br />

(Oncorhynchus spp.) dominated in 2004. Preliminary results for 2003 show no significant within-species<br />

change in energy densities over the breeding season. The mean energy content <strong>of</strong> saury (59.1 kJ/fish +7.4<br />

SEM.), a pelagic species, <strong>and</strong> s<strong>and</strong> lance (69.8 kJ/fish +7.4 SEM.), an inshore species, were not statistically<br />

different, although this may have been due to low power (P = 0.3845). While many other factors influence<br />

foraging efficiency, these results do suggest that saury require birds to travel farther to obtain lower-quality<br />

prey. The importance <strong>of</strong> prey energy content to Rhinoceros Auklet productivity will be further clarified with the<br />

analysis <strong>of</strong> 2004 data.<br />

FORAGING ECOLOGY OF BLACK-CROWNED NIGHT-HERONS IN THE NEW YORK CITY AREA<br />

Andrew J. Bernick* (bernick@mail.csi.cuny.edu); City University <strong>of</strong> New York, Graduate Center/College <strong>of</strong><br />

Staten Isl<strong>and</strong>, Biology Department, Staten Isl<strong>and</strong>, NY USA<br />

Over 1,700 pairs <strong>of</strong> colonial wading birds (e.g., herons, egrets, ibises) breed <strong>and</strong> forage in the<br />

industrialized ecosystem <strong>of</strong> metropolitan New York City. Wading-bird colonies are located on seven isl<strong>and</strong>s<br />

that lie between western Staten Isl<strong>and</strong> <strong>and</strong> Long Isl<strong>and</strong> Sound. The Black-crowned Night-Heron (Nycticorax<br />

nycticorax), a mainly nocturnal forager, is the numerically dominant breeding wader in these colonies <strong>and</strong> has<br />

been undergoing population declines, both locally <strong>and</strong> region-wide. My objective was to determine how Blackcrowned<br />

Night-Herons use marine, freshwater, <strong>and</strong> terrestrial environments in this highly urbanized setting.<br />

From March to September 2004, I conducted weekly surveys on Staten Isl<strong>and</strong>, NY, to describe (1) N. nycticorax<br />

night-time abundance <strong>and</strong> foraging success in four habitat types (shoreline, salt marsh, freshwater, terrestrial);<br />

<strong>and</strong> (2) N. nycticorax foraging flight patterns from an active breeding colony. In 2004, I observed a mean <strong>of</strong> 54<br />

Black-crowned Night-Herons/week foraging at 35 sites on Staten Isl<strong>and</strong>. I found that: (1) a trade<strong>of</strong>f existed<br />

between habitat type <strong>and</strong> foraging success; (2) individuals used different foraging techniques in different<br />

habitats; (3) activity level remained constant over the entire night cycle; <strong>and</strong> (4) the most abundant prey items<br />

available at foraging sites also made up the largest proportion <strong>of</strong> food provisioned to nestlings. By describing<br />

habitat use <strong>and</strong> foraging success for N. nycticorax <strong>and</strong> developing techniques to establish a direct link between<br />

individuals <strong>and</strong> their shifting use <strong>of</strong> foraging habitats, comprehensive conservation <strong>and</strong> management plans for<br />

local wader populations can be developed.<br />

MANAGEMENT OF MARBLED MURRELET POPULATIONS UNDER CANADIAN LAW AND POLICY<br />

Douglas F. Bertram (bertramd@pac.dfo-mpo.gc.ca) <strong>and</strong> David Cunnington; Canadian Wildlife Service,<br />

Institute <strong>of</strong> Ocean Sciences, Sidney, BC CANADA<br />

The Marbled Murrelet is listed by the Committee on the Status <strong>of</strong> Endangered Wildlife in Canada<br />

(COSEWIC) as "Threatened" due to nesting habitat loss <strong>and</strong> threats <strong>of</strong> mortality from oil <strong>and</strong> gill net fishing. In<br />

2003, Canada passed the Species at Risk Act (SARA). The act identifies listed species as Extirpated,<br />

Endangered, Threatened or Special Concern, outlines prohibitions, <strong>and</strong> requires recovery strategies <strong>and</strong> action<br />

plans to be produced. The SARA focuses on the identification <strong>and</strong> conservation <strong>of</strong> "critical habitat" as the basis<br />

for recovery <strong>of</strong> listed species. The SARA places emphasis on l<strong>and</strong> stewardship <strong>and</strong> delegates responsibility for<br />

conservation <strong>of</strong> species on non-federal l<strong>and</strong>s to the provinces <strong>and</strong> territories <strong>of</strong> Canada. The SARA has a "safety<br />

net" which can be invoked if it can be demonstrated that a province or territory has failed to protect a listed<br />

species adequately. In British Columbia, the provincial Wildlife Act <strong>and</strong> the Forest Practices <strong>and</strong> Range Act<br />

address wildlife conservation. However, the BC Forest Practices Review Board has criticized the policies to<br />

conserve Marbled Murrelet habitat in BC on two recent occasions. The Canadian Marbled Murrelet Recovery<br />

Team provides scientific advice to the federal <strong>and</strong> provincial Ministers <strong>and</strong> is responsible for producing a<br />

Recovery Strategy <strong>and</strong> Action Plans. We contrast the conservation <strong>of</strong> Marbled Murrelets under the Canadian<br />

Species at Risk Act with the Endangered Species Act in the USA.

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