Biology and Conservation of American
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Biology and Conservation of American Oystercatchers on the Outer Banks of North Carolina - 20 years of collaborative focal species research and management Ted Simons USGS Cooperative Fish and Wildlife Research Unit Department of Applied Ecology, NC State University Outline • Overview of American Oystercatcher Biology • AMOY Research on the Outer Banks – Changes in Distribution and Abundance – Factors affecting reproductive success • History of American Oystercatcher Working Group Oystercatchers of the Americas Haematopus palliatus Taxonomic Status • Generally recognized as separate species from Haematopus ostralegus • Five subspecies are currently recognized • The subspecies galapagensis, endemic • Regularly hybridizes with to the Galapagos H. bachmani, and hybrids islands, may be a with H. ater are known separate species H. palliatus subspecies • palliatus - Atlantic and Caribbean coasts North America, Central America, South America to southern Brazil, West Indies, and Pacific Central America • durnfordi - Argentina (and Uruguay?) • frazari - W. Mexico • galapagensis - Galapagos Is. • pitanay - W. South America to Chiloe Island, Chile palliatus subspecies Habitats: Diverse, but Strictly Coastal Feeding • Food: almost exclusively shellfish and other marine invertebrates that inhabit intertidal areas. • Foraging microhabitat: restricted to intertidal sand or mud flats, oyster or mussel reefs or shoals; less commonly, rocky shorelines Breeding Biology • Strong mate and nest site fidelity • In North America, the nesting season begins in late March- early May • Oystercatchers lay 2-4 eggs in a shallow scrape • Incubation takes 27 days, during which time the eggs are vulnerable to nest predators, flooding, and exposure • Precocial chicks, 35-45 days to develop flight capability • Unlike most other shorebirds young fed by adults up to 6 weeks after fledging Conservation Status • Globally: Least Concern (IUCN 2007) • US and Canada: Species of Greatest Concern • El Salvador and Mexico: Endangered • Guatemala: Near Threatened • Brazil: Considered Vulnerable in São Paulo state Population estimates: palliatus Distribution Season Individuals Coasts E & S Non-breeding 11,000 USA Mexico Breeding 500 Caribbean Breeding 550 Non-breeding 550 Central Breeding 1751-2450 America Non-breeding 275-600 N South Breeding 200 America Brazil Breeding 6500 palliatus total - 21,326 Clay et al. in Ens, B.J. and L.G. Underhill. 2014. Conservation Status of Oystercatchers around the World. International Wader Studies Number 20. US SHOREBIRD CONSERVATION PLAN SHOREBIRDS OF CONSERVATION CONCERN – 2016 LIST ESA-listed • Black-necked Stilt (knudseni) • Snowy Plover (nivosus [Pacific Coast]) • Piping Plover • Eskimo Curlew • Red Knot (rufa) Greatest Concern • American Oystercatcher (North America breeding palliatus) • Snowy Plover (nivosus [Interior/Gulf Coast] and tenuirostris) • Wilson’s Plover (North America breeding wilsonia) • Mountain Plover • Bristle -thighed Curlew • Bar-tai led Godwit (baueri) • Red Knot (roselaari) Oystercatcher Research in North Carolina • Research began on the Outer Banks in 1997 • Collaborative effort with the NC Wildlife Resources Commission, NPS, USFWS, NC Audubon • Studies of breeding biology now include data from over ~3,000 nesting attempts (~325 breeding pairs) Focal Species Conservation • Widespread along Atlantic and Gulf Coasts • Sensitive to a variety of factors affecting coastal resources – Habitat loss, coastal development – Pressure from human recreation – Pollution – Non -native predators • Large, charismatic, easily identified • Long-lived, amenable to long term mark-resight studies Research Methods • Demographic Studies – Oystercatchers are easily marked, allowing us to identify individuals from year to year and track survival and movement – Each banded Oystercatcher has a unique code engraved on a plastic band that can be read with binoculars or a spotting scope Capture Methods • Adult oystercatchers are captured with a decoy and noose carpet or a “Whoosh” net • Juveniles are captured just before fledging AMOY noose trapping.mov Telemetry • Small chicks tagged with 2g glue-on transmitters • Fledglings and adults are tracked with larger transmitters glued to a leg band • Argos and GPS tags now feasible. Reproductive Success • The breeding season is divided into two distinct periods: nesting and chick rearing • Oystercatcher chicks are mobile shortly after hatch and do not remain in the nest • Nest survival is variable among sites and years, but is generally low; ~25% of all nests survive to hatch • 0.39 (SE 0.02) chicks produced per breeding pair (n = 2,985 nesting attempts, 1995 – 2014) Sources of Nest Failure During Incubation Avian Ghost Crab 5% Human 3% 3% Abandonment 6% Mammal 54% Storm/Tides 29% N = 478 Source of failure could not be determined for 52% of failed nests (N = 518) Sources of Nest Failure – Cape Hatteras Chick Survival • Oystercatcher chicks are camouflaged and highly mobile, which makes them difficult to monitor • We used radio tags to track chicks and identify sources of mortality Chicks Fledged per Breeding Pair 1.4 Cape Hatteras National Seashore Cape Lookout National Seashore 1.2 1 0.8 Productivity 0.6 0.4 0.2 0 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 Year Sources of Chick Mortality Human 16% Environmental 30% Predators 54% N = 37 Source of mortality can not be determined for ~ 50% of chick mortalities 1 0.9 0.8 0.7 0.6 0.5 0.4 0.3 0.2 Cumulative survival probability survival Cumulative 0.1 Schulte, S.A. and T.R. Simons. 2015. Factors affecting the reproductive success of American Oystercatchers 0 (Haematopus palliatus) on the Outer Banks of North 1 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 35 37 39 41 43 45 Carolina. Marine Ornithology 43: 37-47. Days observed Vehicles and Chick Survival • Humans have direct and indirect effects on chick survival • Oystercatcher chicks are highly mobile • Small chicks use truck ruts and beach debris for hiding • Fledglings collide with vehicles at night • 13 chicks killed by vehicles on Hatteras and Lookout from 2003- 2007 • Cape Lookout closed beach sections with oystercatcher broods after two chicks were killed in 2005 • No mortality from vehicles documented on CALO after the policy was implemented Chick Survival and Vehicle Closures 0.6 N=146 0.5 0.4 N=120 0.3 0.2 Survival probability 0.1 0.267 0.476 0 Partial beach Full Beach Closure type Daily survival rates (DSR) for American Oystercatcher broods on beaches with and without off-road vehicles. 1 0.99 0.98 0.97 0.96 DSR 0.95 0.94 0.93 No vehicles present 0.92 Vehicles present 0.91 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 Age (days) Vehicles, Chick Behavior, and Habitat Use FullFull beach beach closures closures Partial beach closures Below tide line Open beach Dunes 22% 26% 39% Chick habitat use Open beach 39% Dunes 74% FullFull beach beach closuresclosures Partial beach closures Resting Resting 24% 31% Out of sight 43% Chick behavior Foraging Out of sight 4% 56% Foraging Moving 10% 16% Getting fed Moving Getting fed 1% 15% 0% Chick Survival - Access to Foraging Sites 1 0.99 0.98 0.97 0.96 DSR 0.95 0.94 0.93 Forage access 0.92 No forage access 0.91 0 3 6 9 12 15 18 21 24 27 30 33 36 39 Age (days) Hurricane Effects • Hurricane Isabel made landfall on the Outer Banks in 2003 • Overwash and sand movement improved habitat and reduced predator populations • Large improvement in reproductive success in areas affected by the storm 0.9 0.8 Hurricane Isabel 0.7 0.6 0.5 0.4 0.3 0.2 Chicks fledged/breeding pair 0.1 0 1999 2000 2001 2002 2003 2004 2005 2006 2007 Hurricane Isabel Overwash Fans 1998 2004 Demographic Model Insights • Hurricanes can have strong positive effects on nest survival • “Bonanza” years may be very important for population stability • Oystercatchers are long-lived birds, so a single strong cohort can have long term effects on the population • Periodic depression of nest predator populations may be an effective management tool for inducing bonanza years Schulte and Simons. 2016. Waterbirds. Predator Management • Gathered baseline data on the ecology of raccoons South Core Banks in 2007 and 2008 – Population size – Home range size – Movement patterns – Population parameters • Age distribution • Survival • Recruitment • Evaluated the response of raccoon, shorebird, and turtle populations to an experimental removal of raccoons in 2008 - 2009 Parsons, A. W., T. R. Simons, A. F. O’Connell, Jr., and M. K. Stoskopf. 2012. Demographics, diet, movements, and survival of an isolated, unmanaged raccoon Procyon lotor (Procyonidae, Carnivora) population on the Outer Banks of North Carolina. Mammalia 77: 21–30. Camera Trapping Results • Total of 1,299 camera “captures” over 5 trapping periods from May 2007 to June 2008 • Total of 532 recaptures • Average population estimate based on photo- recaptures over five camera-trapping periods = 228 animals (SE 20) • Density ~ 10 raccoons per square mile Parsons et al. 2015. Journal of Wildlife Management. Chicks Fledged per Breeding Pair 149 raccoons were trapped and euthanized on South Core Banks in December 2008 and April 2009 Chicks fledgedbreeding per pair Effects of Human Disturbance Objectives: • To assess if military overflights, vehicles, and recreational activities affect the behavior, reproductive success, and survival rates of breeding American Oystercatchers on Cape Lookout National Seashore in 2011 and 2012 Methods: • Baseline audio monitoring of ground noise level across the entire Park • 24- hour continuous audio and video monitoring of American Oystercatcher nests (48,000 hours) • Heart- rate monitoring of incubating Borneman, T.E., E.T. Rose, and T.R. Simons. 2014. Minimal changes in the heart rate of incubating American Oystercatchers individuals (12,000 hours) (Haematopus palliatus) in response to human activity. The Condor 116: 493-503. Behavior of American Oystercatchers Before and During Human Activities * * * * Heart Rate of American Oystercatchers Before and During Human Activities * Limitations of Observational Studies - Lack of true replication, randomization, and controls Table 1.