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International Wader Study Group Annual Conference Den Burg, Texel, the Netherlands, 18–21 September 2009 IWSG Conference Coordinator Jutta Leyrer (left) presenting a token of thanks to Petra de Goeij (right) for leading the organisation of such a successful conference. Photo: Pavel Tomkovich. This was surely a conference of superlatives: record number of delegates (192); record number of countries represented (32); record number of talks (70); superb venue, superb weather and superb organisation! Perhaps the key reason why this conference was such a success is that the organisation was led by Petra de Goeij. Having for many years filled the role of IWSG Conference Coordinator, Petra must be the world’s leading expert on how to organise a successful wader conference. The fact that she had mustered a team of 25 from five nationalities (Dutch, British, German, French and Chinese) suggests that the key to success is careful delegation. Jutta Leyrer, the current IWSG Conference Coordinator, helped Petra with the overall team organisation and supervision. Simon Gillings set up and maintained the conference webpage which for the first time allowed delegates to book and pay for the conference via the IWSG website. Mark Collier, Humphrey Sitters and Yvonne Verkuil worked on acceptance of talks and posters, as well as the editing of abstracts in preparation for the conference programme. Lucie Schmaltz and Hongyan Yang (Nicky) looked after programme books, the registration package, and all sorts of last minute matters. Jos Hooijmeijer, Bob Loos, Bernard Spaans organised the Sunday afternoon excursions to three of the most wonderful wader sites on Texel. Jenny Cremer and Piet van den Hout manned the registration desk. Maurine Dietz and Niko Groen looked after the finances. Roos Kentie and Romke Kleefstra organised a high octane social evening. Anja Cervencl and Anita Koolhaas helped out in all sorts of ways and a team of seven looked after the lecture-halls, projectors, screens, microphones and poster-boards: Geert Aarts, Allert Bijleveld, Maarten Brugge, Anne Dekinga, Sjoerd Duijns, Sander Holthuijsen, and Job ten Horn. A vital contribution to all IWSG conferences is sponsorship, without it their viability and broad appeal would be far less. This year we are most grateful to have received this invaluable support from the African Eurasian Waterbird Agreement, Boere Conservation Consultancy, BIONADE, Natuurmonumenten, Royal Netherlands Institute for Sea Research, Royal Society for the Protection of Birds, Triodos Foundation, and Vogelbescherming Nederland. The conference was held in the modern and comfortable Stayokay Hostel at Den Burg, the main town on Texel. The weather was so good that for much of the weekend we held discussion groups or gathered for coffee or beer outdoors; but the outdoor highlight was the poster session when each presenter took it in turns to speak about their work. The main conference kicked off with the IWSG Annual General Meeting when we were pleased to elect past Chairman Hermann Hötker and past Vice Chairman Theunis Piersma as Honorary Members. It was also agreed to raise Theunis Piersma and Piet van den Hout liven up the social evening. Photo: Pavel Tomkovich. 210 Photo: André Duiven

<strong>International</strong> <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Annual Conference<br />

Den Burg, Texel, the Netherlands, 18–21 September 2009<br />

IWSG Conference Coordinator Jutta Leyrer<br />

(left) presenting a token of thanks to Petra<br />

de Goeij (right) for leading the organisation<br />

of such a successful conference. Photo:<br />

Pavel Tomkovich.<br />

This was surely a<br />

conference of superlatives:<br />

record<br />

number of delegates<br />

(192); record number<br />

of countries<br />

represented (32); record<br />

number of talks<br />

(70); superb venue,<br />

superb weather and<br />

superb organisation!<br />

Perhaps the key<br />

reason why this conference<br />

was such a<br />

success is that the<br />

organisation was led<br />

by Petra de Goeij.<br />

Having for many<br />

years filled the role<br />

of IWSG Conference<br />

Coordinator,<br />

Petra must be the world’s leading expert on how to organise<br />

a successful wader conference. The fact that she had mustered<br />

a team of 25 from five nationalities (Dutch, British, German,<br />

French and Chinese) suggests that the key to success is careful<br />

delegation.<br />

Jutta Leyrer, the current IWSG Conference Coordinator,<br />

helped Petra with the overall team organisation and supervision.<br />

Simon Gillings set up and maintained the conference<br />

webpage which for the first time allowed delegates to book<br />

and pay for the conference via the IWSG website. Mark Collier,<br />

Humphrey Sitters and Yvonne Verkuil worked on acceptance<br />

of talks and posters, as well as the editing of abstracts<br />

in preparation for the conference programme. Lucie Schmaltz<br />

and Hongyan Yang (Nicky) looked after programme books,<br />

the registration package, and all sorts of last minute matters.<br />

Jos Hooijmeijer, Bob Loos, Bernard Spaans organised the<br />

Sunday afternoon excursions to three of the most wonderful<br />

wader sites on Texel. Jenny Cremer and Piet van den Hout<br />

manned the registration desk. Maurine Dietz and Niko Groen<br />

looked after the finances. Roos Kentie and Romke Kleefstra<br />

organised a high octane social evening. Anja Cervencl and<br />

Anita Koolhaas helped out in all sorts of ways and a team<br />

of seven looked after the lecture-halls, projectors, screens,<br />

microphones and poster-boards: Geert Aarts, Allert Bijleveld,<br />

Maarten Brugge, Anne Dekinga, Sjoerd Duijns, Sander<br />

Holthuijsen, and Job ten Horn.<br />

A vital contribution to all IWSG conferences is sponsorship,<br />

without it their viability and broad appeal would be<br />

far less. This year we are most grateful to have received<br />

this invaluable support from the African Eurasian Waterbird<br />

Agreement, Boere Conservation Consultancy, BIONADE,<br />

Natuurmonumenten, Royal Netherlands Institute for Sea<br />

Research, Royal Society for the Protection of Birds, Triodos<br />

Foundation, and Vogelbescherming Nederland.<br />

The conference was held in the modern and comfortable<br />

Stayokay Hostel at Den Burg, the main town on Texel. The<br />

weather was so good that for much of the weekend we held<br />

discussion groups or gathered for coffee or beer outdoors;<br />

but the outdoor highlight was the poster session when each<br />

presenter took it in turns to speak about their work.<br />

The main conference kicked off with the IWSG Annual<br />

General Meeting when we were pleased to elect past Chairman<br />

Hermann Hötker and past Vice Chairman Theunis<br />

Piersma as Honorary Members. It was also agreed to raise<br />

Theunis Piersma and Piet van den Hout liven up the social evening.<br />

Photo: Pavel Tomkovich.<br />

210<br />

Photo: André Duiven


Annual Conference<br />

211<br />

the annual subscription from £22 to £30. The minutes of<br />

the AGM are available on www.waderstudygroup.org, the<br />

IWSG’s website.<br />

Three workshops on popular and thought-provoking<br />

subjects must have contributed to the attraction of the conference<br />

for many of the delegates. The first, which took all<br />

day Friday, was on “Connecting conservation and research”.<br />

It was the brain-child of Jutta Leyrer and was backed with<br />

plenty of encouragement and input from Theunis Piersma. It<br />

sought to address the apparent mismatch and disconnection<br />

between scientific results and advice on the one hand and<br />

conservation and political action on the other. Then on the<br />

Monday there were parallel workshops on “Monitoring waders<br />

in the Siberian arctic” and “The Slender-billed Curlew”.<br />

The first focussed on the problems for wader conservation<br />

of a decline in arctic-based research and its ever-increasing<br />

cost; the second sought to agree plans for a last-ditch attempt<br />

to save what is probably the world’s most endangered wader<br />

from extinction.<br />

The Texel conference of 2009 was one of the best!<br />

Delegates<br />

The Netherlands 60 Poland 4 Norway 2 Kazakhstan 1<br />

United Kingdom 25 Russia 4 Ghana 2 Sweden 1<br />

Germany 25 Spain 3 South Africa 2 Kosovo 1<br />

United States 13 Denmark 3 Italy 2 Mauritania 1<br />

France 9 Estonia 2 Argentina 1 Turkey 1<br />

Portugal 9 Ireland 2 New Zealand 1 Finland 1<br />

Canada 5 Belarus 2 China 1 Iran 1<br />

Australia 4 Czech Republic 2 Ukraine 1 Belgium 1<br />

Abstracts of Conference Talks<br />

Migration and stopover ecology<br />

Why have Red Knots, Ruddy Turnstones and<br />

Sanderlings reacted differently to the decline in the<br />

availability of horseshoe crab eggs in Delaware Bay<br />

Humphrey Sitters 1 , Larry Niles 2 , Amanda Dey 3 ,<br />

Kevin Kalasz 4 , Allan Baker 5 , Kathy Clark 3 , Nigel Clark 6 ,<br />

Dick Veitch 7 & Clive Minton 8<br />

1 Limosa, Old Ebford Lane, Ebford, Exeter, UK<br />

hsitters@aol.com<br />

2 Conserve Wildlife New Jersey, 516 Farnsworth Avenue,<br />

Bordentown, New Jersey, USA<br />

3 New Jersey Division of Fish and Wildlife, New Jersey, USA<br />

4 Delaware Division of Fish & Wildlife, Delaware, USA<br />

5 Royal Ontario Museum, Toronto, Canada<br />

6 British Trust for Ornithology, UK<br />

7 Papakura, New Zealand<br />

8 Australasian <strong>Wader</strong> Studies <strong>Group</strong>, Australia<br />

Red Knots Calidris canutus, Ruddy Turnstones Arenaria<br />

interpres and Sanderlings Calidris alba all feed on horseshoe<br />

crab eggs in Delaware Bay, but the reaction of each species<br />

to the decline in egg availability has been different. Over<br />

1998–2008, numbers of Knots and Turnstones using Delaware<br />

Bay declined by 60–70% though Sanderlings showed<br />

no clear trend. The flyway population of Knots has declined,<br />

but (on the basis of rather sparse data) those of Turnstones and<br />

Sanderlings have not. The decline in crab eggs has affected<br />

these species in different ways, because of differences in<br />

feeding ecology and migratory strategy. All three take eggs<br />

from the sand surface and Knots and Sanderlings take buried<br />

eggs by probing, but Turnstones use their stout bills to dig<br />

pits to gain access to buried egg-clusters. Sanderlings are<br />

less dependent on eggs in Delaware Bay and commonly take<br />

other prey. Knots have shown a strong year-on-year trend<br />

to lower weights at the end of the stopover, turnstones have<br />

been less affected and Sanderlings not at all. Turnstones may<br />

be less dependent on eggs than Knots because they are relatively<br />

short-distance migrants. Many Knots winter in Tierra<br />

del Fuego and, as such, are subject to greater physiological<br />

constraints.<br />

Global climate change and the migration of<br />

Hudsonian Godwits Limosa haemastica<br />

Nathan R. Senner<br />

Department of Ecology and Evolutionary Biology,<br />

Cornell University, USA. nrs57@cornell.edu<br />

Much recent work has attempted to determine the events<br />

that most influence the duration, speed, and timing of longdistance<br />

bird migration in the context of global climate<br />

change. The majority of these studies have identified largescale<br />

processes, such as the North Atlantic Oscillation, or<br />

regional-scale correlates of phenology and productivity,<br />

such as the Normalized Difference Vegetation Index, as the<br />

primary variables explaining ongoing changes in the timing<br />

of bird migration, but they have largely ignored the role of<br />

local-scale weather patterns as potential drivers of change.<br />

Using historical arrival data and both large and small-scale<br />

weather and climatic variables from throughout the ranges<br />

of two breeding populations of Hudsonian Godwits, Limosa<br />

haemastica in Hudson Bay and Alaska, we built a model to<br />

formulate a set of testable hypotheses explaining the yearto-year<br />

variation and long-term trends in arrival times in<br />

these two populations. We tested this model using spatial<br />

and temporal location data for the Hudson Bay breeding


212 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

population, acquired from a cohort of adults carrying British<br />

Antarctic Survey data-loggers. Our preliminary analysis<br />

suggests that despite using a similar migration corridor,<br />

significantly different climactic and weather factors impact<br />

the migrations of these two populations. These differences<br />

may suggest that these two populations will have differing<br />

capabilities to respond to future changes in global climatic<br />

regimes and to continue to accurately time their migrations<br />

with shifts in insect phenology at their Arctic and sub-arctic<br />

breeding grounds. Our future work will focus on expanding<br />

our analysis to include similar location data from the Alaskan<br />

breeding population as well.<br />

New insights from stable isotopes:<br />

do Red Knots Calidris canutus islandica<br />

pass Iceland by during southward migration<br />

Maurine Dietz 1 , Bernard Spaans 2 , Anne Dekinga 2 ,<br />

Marcel Klaassen 3 , Harry Korthals 3 ,<br />

Casper van Leeuwen 3 & Theunis Piersma 1,2<br />

1 Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies, University of Groningen, PO Box 14,<br />

9750 AA Haren, the Netherlands; m.w.dietz@rug.nl<br />

2 Department of Marine Ecology, Royal Netherlands Institute<br />

for Sea Research (NIOZ), PO Box 59,<br />

1790 AB Den Burg, Texel, the Netherlands.<br />

3 Department of Plant–Animal Interactions, Centre for<br />

Limnology, Netherlands Institute of Ecology (NIOO–KNAW),<br />

PO Box 1299, 3600 BG Maarssen, the Netherlands<br />

The Red Knot subspecies Calidris canutus islandica breeds<br />

on the Arctic tundras in NE Canada and N Greenland and<br />

winters along the coasts in NW Europe. Islandica Knots<br />

stopover during northward migration in Iceland or N Norway<br />

and during southward migration in Iceland, though some<br />

birds (mainly juveniles) are found in Norway and Denmark.<br />

At about 4,800 km, this migration route is the shortest of<br />

all six knot subspecies. Islandica Knots may be able to fly<br />

this distance in one flight because migration flights of the<br />

other subspecies can be as long as 6,900 km. Using stable<br />

carbon isotopes ratios (δ 13 C) in blood (cells) and plasma, we<br />

investigated evidence for a stopover in Iceland en route to<br />

the Dutch Wadden Sea. Considering the expected duration<br />

of stopover at Iceland (12–15 d, max 17 d) and the turnover<br />

rates of blood (cells; 15.07 d) and plasma (6.03 d), Red Knots<br />

should arrive after a stopover in Iceland with δ 13 C ratios in<br />

plasma approaching the marine diet and blood (cells) ratios<br />

midway between the tundra and marine signal. Many adults<br />

had δ 13 C ratios in blood (cells) and plasma below this expectation<br />

and some Knots even had tundra signals in their<br />

blood (cells); a strong indication that adults pass Iceland<br />

by. Remarkably, also juveniles arrived with tundra signals<br />

in blood (cells), indicating that they also pass Iceland by en<br />

route to the wintering grounds. This contradicts the general<br />

idea that juvenile shorebirds have more stopovers than adults.<br />

The δ 13 C signature of second-year birds confirmed that they<br />

had oversummered in the Wadden Sea. Because islandica<br />

Knots arrive with tundra δ 13 C signatures in the Wadden Sea,<br />

δ 13 C ratios can be used to estimate time since arrival, making<br />

it possible for the first time to construct a detailed arrival<br />

schedule for knots in their wintering areas. We can now look<br />

at, for example, the variation in body and gizzard mass, and<br />

body mass change with time since arrival.<br />

Habitat choice of Afro-Siberian Red Knots<br />

Calidris canutus canutus in the Schleswig-Holstein<br />

Wadden Sea during northward migration<br />

Anne Schrimpf, Jutta Leyrer, Maarten Brugge,<br />

Anne Dekinga & Theunis Piersma<br />

Royal NIOZ, PO Box 59, 1790AB Den Burg,<br />

Texel, the Netherlands; Anneffm@web.de<br />

The Schleswig-Holstein Wadden Sea, Germany, is an important<br />

stop-over site for migrating waders and waterbirds. During<br />

northward migration birds have a tight schedule in order<br />

to arrive at their breeding ground at the optimal time. Arriving<br />

too early increases the risks of lack of snowfree ground and<br />

food upon arrival on the tundra, whereas arriving too late may<br />

compromise breeding success. Conditions at the last stop-over<br />

sites in particular, will influence survival and reproductive<br />

chances later on. Afro–Siberian Red Knots Calidris canutus<br />

canutus winter in W Africa and breed in northernmost Taymyr<br />

peninsula, Siberia. They cover this distance in two 4,500 km<br />

long non-stop flights, with the Schleswig-Holstein Wadden<br />

Sea as the main stop-over site. During the 2–3 weeks spent<br />

there, the birds have to double their mass in order to have<br />

enough surplus energy stores to ensure their survival after<br />

arrival on the breeding grounds. Outside the breeding season,<br />

Red Knots feed on molluscs ingested whole, with thin-shelled<br />

prey such as Macoma baltica being preferred. From 2006 to<br />

2009, we studied Red Knot diet and prey abundance in the<br />

Schleswig-Holstein Wadden Sea during northward migration<br />

comparing an area in Nordfriesland (where prey were<br />

dominated by cockles Cerastoderma edule and mud snails<br />

Hydrobia ulvae, which are of rather low quality for Red<br />

Knots), and one in Dithmarschen (where Macoma was more<br />

common). Afro–Siberian Red Knots seem to converge into<br />

the Dithmarschen area before departure, probably on account<br />

of the better prey quality. Nevertheless, their food there is<br />

not secure, because the density and quality of Macoma has<br />

decreased over the last four years. The decline in quality is<br />

caused by an increased shell length and a lack of small individuals.<br />

We also found high annual variability in the density<br />

and quality of Cerastoderma and Hydrobia.<br />

Stopover ecology of first-year Wood Sandpipers<br />

on their autumn migration<br />

Piotr Minias 1 , Radosław Włodarczyk 1 ,<br />

Krzysztof Kaczmarek 2 & Tomasz Janiszewski 1<br />

1 Department of Teacher Training and Biodiversity<br />

Studies, University of Łódź, 1/3 Banacha, 90-237 Łódź,<br />

Poland; pminias@op.pl<br />

2 Medical University of Łódź, 4 Kosciuszki, Łódź, Poland<br />

Wood Sandpipers Tringa glareola were trapped at Jeziorsko<br />

reservoir, central Poland during Jul–Sep, 1997–2007. About<br />

4,400 first-year Wood Sandpipers were caught and 264 were<br />

retrapped within the year of ringing, allowing calculation<br />

of fat accumulation rates. These decreased as the season<br />

progressed; however, length of stay was constant throughout<br />

the whole migration period. The value of fat loads already<br />

accumulated by individual birds was negatively correlated<br />

with both the rate of subsequent fat accumulation and the<br />

period between capture and recapture. There was considerable<br />

inter-seasonal variation in the mean length of the staging<br />

period, which was related to differences in feeding conditions


Annual Conference<br />

213<br />

between years. The results indicate that first-year Wood Sandpipers<br />

follow a time-minimization migration strategy only<br />

when feeding conditions at the stopover site are favourable.<br />

In the seasons when feeding conditions were unfavourable,<br />

the birds modified their migration strategy, as they probably<br />

could not attain optimal fuel stores in a sufficiently short<br />

period of time.<br />

Stopover vs. staging sites:<br />

a difference between a hop and a jump<br />

Nils Warnock<br />

Wildlife Health Center, School of Veterinary Medicine,<br />

University of California, Davis, CA 95616, USA<br />

ndwarnock@ucdavis.edu<br />

In the past decade, more sophisticated methods to track<br />

birds combined with calls for understanding the connectivity<br />

between breeding and non-breeding areas have generated<br />

detailed studies describing the migration routes of birds with<br />

additional focus on intermediary sites that birds use during<br />

their migrations. Sites that birds stop at during migration<br />

have been described in various ways, but increasingly these<br />

areas are described as stopover and/or staging sites. These<br />

terms are often used interchangeably to mean a place where<br />

birds stop during their migration. Attempts have been made<br />

to distinguish between the two terms, but consistency in use<br />

and definition still varies significantly. Given the diversity<br />

of use of these two terms, I present ideas on how stopover<br />

and staging sites might differ in ecological function from the<br />

perspective of migrating birds and suggest conservation implications<br />

for distinguishing between these two types of sites.<br />

I argue that while all sites where birds rest and feed during<br />

migration qualify as stopover sites, not all stopover sites<br />

qualify as staging sites. In fact, there are probably relatively<br />

few true staging sites in the world, and given the conservation<br />

importance of identifying these important migratory sites,<br />

understanding the function of staging sites is important.<br />

Habitat selection and prey quality of Red Knots<br />

during spring stopover in Virginia, USA<br />

Jonathan B. Cohen 1 , Sarah M. Karpanty 1 ,<br />

James D. Fraser 1 & Barry R. Truitt 2<br />

1 Dept. Fisheries and Wildlife, Virginia Tech. Virginia, USA<br />

jocohen1@vt.edu<br />

2 The Nature Conservancy, Virginia, USA<br />

Although Delaware Bay is the most renowned spring stopover<br />

site for Red Knots in the United States, 6,000–10,000 knots<br />

have been counted on the Virginia Coast. Unlike in Delaware<br />

Bay, Red Knots in Virginia do not have horseshoe crab eggs<br />

on which to forage. We examined the relationship between the<br />

distribution of Red Knots and potential prey items in Virginia,<br />

2006–2008. Red Knots foraging in the sandy intertidal zone<br />

selected patches with more crustaceans than random plots,<br />

and flock-size was positively correlated with abundance and<br />

size of coquina clams Donax variabilis. However, the quality<br />

of coquina clams was low, as measured by the ratio of energetic<br />

content to shell mass. Red Knots foraging on peat banks<br />

were associated with patches of blue mussels Mytilus edulis<br />

and false angel wings Petricola pholadiformis. These bivalves<br />

were of somewhat higher quality than coquina clams, but still<br />

of low quality. Concurrent research has indicated that very<br />

few Red Knots using Virginia as a stopover site continue to<br />

the Delaware Bay. To better understand the value of Virginia<br />

to Red Knots, future studies should focus on determining the<br />

wintering ground origins of Red Knots stopping in Virginia,<br />

and their survival and reproductive success.<br />

Foraging ecology<br />

Basal metabolic rate increases with salinity<br />

in a long-distance migratory shorebird<br />

Jorge S. Gutiérrez, José A. Masero,<br />

José M. Abad-Gómez, Auxiliadora Villegas &<br />

Juan M. Sánchez-Guzmán<br />

Conservation Biology Research <strong>Group</strong>, Zoology,<br />

University of Extremadura, Avenida de Elvas s/n, 06071<br />

Badajoz, Spain; jorgesgutierrez@unex.es<br />

Avian basal metabolic rate (BMR) may be viewed as a highly<br />

flexible physiological trait influenced by environmental factors.<br />

Many long-distance migratory shorebirds switch from a<br />

diet of terrestrial invertebrates during the breeding season to a<br />

diet of intertidal invertebrates during winter, and phenotypic<br />

flexibility in BMR may represent an important component<br />

of short-term acclimation to saline environments. In this<br />

study we tested experimentally the effects of water salinity<br />

on BMR of captive Dunlins Calidris alpina caged in outdoor<br />

aviaries. We measured the oxygen consumption of Dunlins<br />

under three different salt water regimes: fresh water (FW;<br />

0.3±0.0‰), brackish water (BW; 10.4±0.5‰) and saline<br />

water (SW; 30.1±2.1‰). We found that both whole-organism<br />

and mass-specific BMR increased by 8% and 17% from FW<br />

to SW, respectively. These changes were quickly reversed by<br />

returning the birds to fresh water. Our findings showed that a<br />

small-sized shorebird, like Dunlin, is able to modify its BMR<br />

in response to an increase in salinity adjusting its “osmoregulatory<br />

machinery” to maintain osmotic equilibrium. The<br />

significant increase in BMR associated with salinity could<br />

be explained by an increase in organs such as the salt gland.<br />

Cryptic competition for safe foraging sites<br />

in a gregarious shorebird<br />

Piet van den Hout 1 , Tamar Lok 1 , Bernard Spaans 1 &<br />

Theunis Piersma 1,2<br />

1 Royal Netherlands Institute for Sea Research, Texel,<br />

the Netherlands; hout@nioz.nl<br />

2<br />

Center for Ecological and Evolutionairy Studies,<br />

University of Groningen, the Netherlands<br />

Many species benefit from flocking as one of the measures<br />

to manage predation danger. Although all individuals may<br />

attempt to gain optimal benefits from such flocks, not all<br />

birds manage to do so as they may lack sufficient competitive<br />

abilities. Contrary to some contexts, such as territoriality,


214 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

klepto-parasitism, and foraging at high densities, which are<br />

characterized by visible interactions, patterns of competition<br />

are often elusive to direct observation. In this study we show<br />

that during their lifetime individual Red Knots Calidris c. canutus<br />

gradually shift to safer foraging conditions. We provide<br />

evidence that competition for safety is a life-long issue for<br />

Red Knots. We argue that such cryptic competition patterns<br />

may govern animal densities and distributions at a wide<br />

range of spatial scales, possibly even affecting geographical<br />

gradients in sex and age-ratios.<br />

Stable isotope approach to studying the feeding<br />

strategy of Black-tailed Godwits Limosa limosa<br />

islandica wintering along the French Atlantic coast<br />

Frédéric Robin 1 , Philippe Delaporte 2 , Francis Meunier 3 ,<br />

Camille Fontaine 1 & Pierrick Bocher 1<br />

1 Laboratory of Coastal Environnement and Societies UMR<br />

LIENSs 6250 CNRS, Universisity of La Rochelle, 17000,<br />

France; frobin02@univ-lr.fr<br />

2<br />

Nature Reserve of Moëze-Oléron, Ligue pour la protection<br />

des oiseaux LPO, Ferme de Plaisance, Saint-Froult 17780,<br />

France<br />

3<br />

Ligue pour la protection des oiseaux LPO,<br />

La corderie Royale, Rochefort 17305, France<br />

For coastal waders, an adequate food resource is essential in<br />

the choice of wintering habitats and sites. Those studies of<br />

wintering strategies that deal with the dietary aspect use several<br />

approaches, including fecal analysis and prey sampling<br />

in feeding areas, to assess their quality. The stable isotope<br />

ratio δ 15 N:δ 13 C is a complementary method for comparing<br />

diet between wintering sites and for measuring variation<br />

throughout the winter period. This qualitative approach also<br />

has the potential to determine the origin of birds over a short<br />

time-scale. We used this method to describe the wintering<br />

strategy of Black-tailed Godwits on the central Atlantic<br />

coast of France. During fieldwork carried out between July<br />

2008 and April 2009, >300 samples of godwit blood and<br />

feather were collected at four sites in the South Vendée and<br />

Charente-maritime: the Ré island, and the bays of Aiguillon,<br />

Yves, and Marennes-Oléron. Feathers and blood were collected<br />

each month when godwits were caught at high tide<br />

roost and prey species were sampled from the feeding areas<br />

to connect the food resources to the birds’ diets. The results<br />

show that juvenile feather signatures have a terrestrial origin<br />

while adult feathers have a saline origin. Over the wintering<br />

period, blood samples show an estuarine signature but<br />

variability in the isotope ratio from prey species between<br />

sites shows that some godwits might shift sites more or less<br />

frequently over the course of the winter. Temporal analysis<br />

of these data allows us to describe the phenology of the use<br />

of the different feeding habitats.<br />

The macrozoobentos of the Sivash<br />

is the main feeding base for tundra waders in the<br />

south of the Ukraine during migration<br />

Tatyana Kirikova<br />

Azov–Black Sea Ornithological Station, Lenin Str., 20,<br />

Melitopol, Zaporizhzhia region, 72312 Ukraine<br />

azov.black.station@gmail.com<br />

This study, covering 1994–2002, provides the first estimation<br />

of the food reserves available to migrant arctic waders in the<br />

eastern and central parts of the Sivash wetlands of southern<br />

Ukraine.<br />

Forty species of the macrozoobenthos were recorded in<br />

the shallow waters of the Sivash; of these 39% have been<br />

recorded as taken by waders. Long-term average annual biomass<br />

of marcozoobenthos wader food in the Eastern Sivash<br />

was 12.14 g/m 2 in spring and 14.57 g/m 2 in autumn; in the<br />

Central Sivash, it was 6.03 g/m 2 in spring and 5.30 g/m 2 in<br />

autumn. These are relatively low values compared with other<br />

wader stopover sites in the south of the Ukraine.<br />

In the Eastern Sivash, most of the biomass of wader food<br />

consisted of polychaetes. Generally, the autumn biomass of<br />

polychaetes was higher than in spring. Insect larvae and Gastropods<br />

also made substantial contributions to the biomass.<br />

In spring the largest contribution to the energetic value of<br />

macrozoobenthic food in the Eastern Sivash was Gastropods;<br />

in autumn it was polychaetes. Over the study period, we<br />

noted a tendency for the biomass and energetic contribution<br />

of polychaetes to decrease and for that of Chironomid larvae<br />

to increase.<br />

The main biomass and energetic content of food resources<br />

in the Central Sivash consisted of Chironomid larvae and<br />

brine shrimps (Artemia). Generally the density of wader food<br />

resources was higher in the Eastern Sivash than in the Central<br />

Sivash, but the reverse occurred in 1997.<br />

In the Eastern Sivash, food reserves available to waders<br />

in autumn doubled during the study period because of<br />

an increasing trend for lower water levels due to wind and<br />

evaporation. In the Central Sivash under the same conditions<br />

food reserves increased on 17 occasions.<br />

The total energy requirements of waders staging in the<br />

Eastern Sivash during autumn migration were greater than<br />

in spring. The total energy requirements of waders staging<br />

in the Central Sivash were generally lower than those staging<br />

in the Eastern Sivash.<br />

The estimated food resources available for waders in the<br />

Eastern Sivash in spring were over 20 times greater than<br />

the waders’ requirements when water levels were at their<br />

maximum, but over 30 times greater when water levels were<br />

at a minimum. In autumn, resources exceeded wader energy<br />

requirements by factors of 6.2 and 10.9 respectively. During<br />

spring migration, the Central Sivash is estimated to provide<br />

waders with only 5–15% of the energy they need when water<br />

level are at a maximum, but when water levels are low food<br />

reserves are 1.1–3.7 times greater than their requirements.<br />

A wader food deficit was also found during autumn migration<br />

in the Central Sivash when water levels were at a<br />

maximum. Only 35.4 % of their needs could be met from the<br />

energy of available benthic biomass. This problem is partly<br />

solved when water fall and the food reserves become on average<br />

5.7 times greater than wader requirements.<br />

Unfavorable food conditions in the Central Sivash were<br />

a reason for the movement of waders to the Eastern Sivash<br />

where generally more food is available.<br />

In view of the high total energy reserves of macrozoobenthic<br />

wader food in the Eastern Sivash (and the ability of<br />

waders to fly), it can be concluded that the Sivash can provide<br />

enough stopover food resources in any season of the year. The<br />

lagoon system of the Sivash therefore plays a vital role in<br />

supporting important populations of arctic migratory waders.


<strong>Wader</strong> hotspots and monitoring<br />

215<br />

The AWSG and its relevance<br />

in the East Asian–Australasian Flyway<br />

Ken Gosbell, Clive Minton & Danny Rogers<br />

Australasian <strong>Wader</strong> Studies <strong>Group</strong>, Australia;<br />

ken@gosbell.id.au<br />

Australia and New Zealand are important non-breeding areas<br />

for migratory wader populations that utilize the East Asian<br />

– Australasian Flyway (EAAF) to reach breeding areas in<br />

Siberia and Alaska. Thirty-three wader species spend the<br />

non breeding period in Australasia. These have been studied<br />

by the Australasian <strong>Wader</strong> Studies <strong>Group</strong> (AWSG) and other<br />

regional groups in Australia for >30 years. Studies have<br />

included banding and leg flagging programs, population<br />

monitoring and extensive training activities for both local<br />

and Asian participants. Being at the end of the flyway affords<br />

opportunities to study many aspects of the populations of<br />

Arctic breeding waders. Banding studies initially focused<br />

on biometrics and moult as well as on migration routes and<br />

destinations. With the introduction of coloured leg-flags in<br />

1990, knowledge of migration routes and stopover locations<br />

increased enormously. A comprehensive leg-flag sighting<br />

database was developed and this currently has >17,000<br />

records from throughout the flyway.<br />

With the increased need to understand the demographic<br />

factors influencing wader populations, more recent studies<br />

have focussed on the assessment of breeding success, as<br />

measured by the proportion of juveniles, and collection of<br />

data to measure survival rates. The AWSG have collected<br />

population data from a number of important sites from around<br />

Australia for the last 29 years; this provides the only comprehensive<br />

long term dataset on wader numbers available to<br />

planners and government agencies. The increased need for the<br />

early identification of trends has led to the development of a<br />

more comprehensive and robust monitoring program entitled<br />

Shorebirds 2020. Again, a comprehensive database has been<br />

developed incorporating historical AWSG data. Preliminary<br />

analyses have shown that several migratory species such as<br />

Curlew Sandpiper and Red Knot have suffered extensive<br />

declines over the last decade. Over the same period, studies<br />

have shown that the Yellow Sea, bounded by China and the<br />

Korean Peninsula, is the single most important stopover site<br />

for migratory shorebirds; an estimated 2 million (40% of the<br />

flyway total) are critically dependant on this region during<br />

northward migration.<br />

Many shorebird populations are declining globally and in<br />

the EAAF five species are classified as threatened and nine<br />

populations are in decline. Unfortunately this area continues<br />

to suffer extensive habitat loss due to ever-increasing development<br />

and reclamation. Almost half the total intertidal areas<br />

of the Chinese and South Korean coast have been destroyed.<br />

A monitoring program in Australia, MYSMA (Monitoring<br />

Yellow Sea Migrants in Australia) is now demonstrating<br />

marked reductions in populations of some species as a consequence<br />

of this destruction. The AWSG has undertaken<br />

monitoring and training programs in this region in collaboration<br />

with local governments and NGOs. Future studies will<br />

include the use of recently-developed technologies to help<br />

study movements while the Shorebirds 2020 program will<br />

enable a more rigorous assessment of population trends for<br />

key species. As a partner in the EAAF Partnership, the AWSG<br />

collaborates with key countries such as China and Korea to<br />

achieve a more sustainable development ethic within the<br />

Yellow Sea region.<br />

Estimating eastern Pacific coast populations of<br />

Whimbrels and Hudsonian Godwits,<br />

with an emphasis on Chiloé Island, Chile<br />

Brad A. Andres, James A. Johnson, Jorge Valenzuela,<br />

R.I. Guy Morrison, Luis A. Espinosa & R. Ken Ross<br />

U.S. Fish and Wildlife Service, Division of Migratory Bird<br />

Management, PO Box 25486, DFC-Parfet, Denver, CO,<br />

80225-0486, USA; Brad_Andres@fws.gov<br />

A large proportion of the Hudsonian Godwits Limosa haemastica<br />

spending the boreal winter along the eastern Pacific<br />

Ocean coast are known to occur in the vicinity of Chiloé<br />

Island, Chile, but the importance of the region to Whimbrels<br />

Numenius phaeopus is less known. Ground counts conducted<br />

in 2007 and 2008 increased published estimates, at a<br />

minimum, of Pacific coast populations by 27% for Whimbrels<br />

(33,150 individuals) and 51% for Hudsonian Godwits (21,161<br />

individuals). Bays and shorelines in the Chiloé Island region<br />

supported 99% of Hudsonian Godwits and, perhaps, 61% of<br />

Whimbrels estimated to occur along the Pacific coast during<br />

the boreal winter. Whereas Hudsonian Godwits aggregated<br />

in shallow bays on the eastern and northern coast of Chiloé<br />

Island, Whimbrels were more dispersed along the island’s<br />

coastline and reached a density of 7.5 birds/km along sheltered<br />

gravel shorelines. Bays in the vicinity of Chiloé’s capital,<br />

Castro, provided important foraging and roosting habitat<br />

for non-breeding birds; these sites supported 52% the of the<br />

Pacific coast population of Hudsonian Godwits and >4,000<br />

Whimbrels. Low human disturbance in Pullao and Putemün<br />

bays make these sites particularly attractive to non-breeding<br />

Hudsonian Godwits, and their permanent protection is urged.<br />

Searching for a needle in a haystack:<br />

surveying wintering Spoon-billed Sandpipers in the<br />

Gulf of Martaban (Myanmar)<br />

Nigel A. Clark 1 , Nathan Hentze, Vladimir Morozov,<br />

U Thet Zaw Naing, Daw Nilar Pwint & Christoph Zockler<br />

1 British Trust for Ornithology, Thetford, Norfolk, IP24 2PU,<br />

UK; nigel.clark@bto.org<br />

During January 2009 a team of ornithologists spent two<br />

weeks surveying the extensive intertidal flats of the Gulf of<br />

Martaban, Mynamar, for Spoon-billed Sandpipers and other<br />

waterbirds. It was only possible to move around the estuary<br />

in relatively slow-moving boats settling on the flats at low<br />

tide and surveying on foot. It was not possible to move along<br />

the saltmarshes from the land and in most places it was not<br />

possible to approach from a boat as the water was too shallow<br />

and the substrate too soft. As a result, estimating the numbers<br />

of Spoon-billed Sandpipers had to be done through low-tide<br />

surveys which only covered part of the estuary. A range of<br />

analytical methods were investigated to predict the number<br />

of Spoon-billed Sandpipers wintering on the site. It is hoped<br />

that the results will aid future surveys in other parts of the<br />

potential wintering range.<br />

215


216 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

Distribution, breeding and wintering abundances,<br />

and seasonal occurrences of waders<br />

in the Gediz Delta, Western Turkey<br />

Ortaç Onmuş 1 & Mehmet Siki 2<br />

1<br />

Faculty of Sciences, Department of Biology,<br />

Ege University, Izmir, Turkey; ortac.onmus@ege.edu.tr<br />

2<br />

Natural History Museum, Research and Application Centre<br />

The Gediz Delta is a Ramsar site in the Aegean coast of<br />

Turkey with about 35 km of sea-coast. The aim of this study<br />

was to describe the distributions, breeding and wintering<br />

abundances, and seasonal occurrences of waders in the Gediz<br />

Delta. Data on breeding waders were obtained from two<br />

atlas mapping studies conducted in 2002 and 2006. The atlas<br />

study area included 305 1×1 km square UTM grids. Three<br />

10-minute point-counts were carried out within each of these<br />

squares sampling for breeding activity and relative abundance<br />

of birds, as well as habitats and threats. Standard EBCC<br />

breeding codes were used to describe breeding activities. The<br />

minimum and maximum number of apparently occupied nests<br />

was also counted during the atlas studies. Data on wintering<br />

abundances were obtained from nine different waterbird<br />

censuses (IWC) carried out between 1990 and 2007. Seasonal<br />

occurrence was determined using data from 314 visits covering<br />

all weeks of the year and carried out between 1994 and<br />

2007. Breeding evidence was obtained for nine species in<br />

2002 and eight in 2006. These were Eurasian Oystercatcher<br />

Haematopus ostralegus, Black-winged Stilt Himantopus<br />

himantopus, Pied Avocet Recurvirostra avosetta, Eurasian<br />

Stone-curlew Burhinus oedicnemus, Collared Pratincole<br />

Glareola pratincola, Little Ringed Plover Charadrius dubius,<br />

Kentish Plover Ch. alexandrinus, Spur-winged Plover Vanellus<br />

spinosus, and Redshank, Tringa totanus. The total number<br />

of wintering species was 28; among these, 13 were classified<br />

as regular, 7 as occasional and 8 as rare. During 314 visits<br />

between 1994 and 2007, the total number of species identified<br />

was 39. The Gediz Delta is one of the most important<br />

wetlands for breeding and wintering waders in Turkey and<br />

supports a good representation of the wader species occurring<br />

in the country.<br />

Population dynamics – habitat selection<br />

Population dynamics of Piping Plovers<br />

Charadrius melodus using engineered and natural<br />

sandbars on the Missouri River<br />

Daniel H. Catlin, Joy H. Felio, Jonathan B. Cohen &<br />

James D. Fraser<br />

Department of Fisheries and Wildlife Sciences,<br />

Virginia Polytechnic Institute and State University,<br />

Blacksburg, Virginia, USA; dcatlin@vt.edu<br />

In 2004, the US Army Corps of Engineers began engineering<br />

sandbar habitat in response to habitat limitation for the<br />

threatened Piping Plover Charadrius melodus. Beginning<br />

in 2005, we compared the fates of nests, broods, and adults<br />

on natural sandbars with those on engineered sandbars. We<br />

monitored 623 nests from which we banded 357 adults and<br />

694 chicks to investigate the factors affecting nest survival,<br />

juvenile and adult survival, and movement. Nesting adult<br />

plovers selected for engineered habitats; there were more<br />

nests initiated on engineered habitat than would be expected<br />

based on area, nesting birds were more likely to move to<br />

engineered sandbars than to natural sandbars, and nesting<br />

densities on engineered sandbars were approximately seven<br />

times as high as on natural sandbars. Furthermore, nesting<br />

success was higher on engineered habitat than on natural<br />

habitat. Prefledging survival was similar, on average, between<br />

natural and engineered sandbars, but chick survival<br />

on engineered sandbars was highly variable. Postfledgling<br />

survival also was similar on the two sandbar types, but<br />

fidelity to study area was lower for birds hatched on natural<br />

habitat. In general, engineered habitat was more productive<br />

than the natural habitat, but the productivity on these sandbars<br />

decreased with age. Management for population growth<br />

should include considerations of habitat availability, nesting<br />

densities, amount of foraging habitat, and the effects of water<br />

management on these factors. It appears that appropriately<br />

timed and controlled addition of engineered habitat could<br />

contribute to recovery efforts, but continued investigation of<br />

the longevity of engineered habitat is required.<br />

Local changes cause global shifts:<br />

eastward relocation of migration routes and<br />

breeding sites in Ruff Philomachus pugnax<br />

Eldar N. Rakhimberdiev 1 , Yvonne I. Verkuil 2,3 ,<br />

Anatoly A. Saveliev 4 , Pavel S. Tomkovich 5 &<br />

Theunis Piersma 1,6<br />

1 Department of Vertebtate Zoology, Biological Faculty,<br />

Moscow State University, 119991, 1 Leninskiye gory,<br />

Moscow, Russia; eldarrak@gmail.com<br />

2 Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies, University of Groningen, PO Box 14,<br />

9750 AA Haren, the Netherlands<br />

3 Dept. of Natural History, Royal Ontario Museum,<br />

100 Queen’s Park Crescent, Toronto, M5S 2C6, Canada<br />

4 Geography and Ecology Faculty, Kazan State University,<br />

420008, 18 Kremlevskaja Street, Kazan,<br />

The Russian Federation<br />

5 Zoological Museum, Moscow State University,<br />

Bolshaya Nikitskaya Str., 6, Moscow, Russia<br />

6 Department of Marine Ecology, Royal Netherlands Institute<br />

for Sea Research (NIOZ), PO Box 59, 1790 AB Den Burg,<br />

Texel, the Netherlands<br />

In W Europe, there has been a steep decline in the number<br />

of migrating Ruff over the last two decades. This raises<br />

questions about probable recent changes in the breeding<br />

population. We have analyzed recent monitoring data from<br />

the Arctic, where over 90% of the global Ruff population<br />

breeds (online database www.arcticbirds.net, maintained<br />

by Mikhail Soloviev and Pavel Tomkovich). Generalized<br />

Additive Modeling and Generalized Estimations Equations<br />

methods detect changes in the population dynamics of breeding<br />

Ruffs. While in the European Arctic Ruffs have been<br />

decreasing during the last 18 years, in W Siberia Ruffs have<br />

increased. Our results corroborate the increasing numbers of<br />

Ruffs migrating through Eastern Europe (Belarus), which<br />

suggests a growing preference for the E Europe migration<br />

corridor, with its terminal point in W Siberia. We assume that


Annual Conference<br />

217<br />

local changes in agricultural activity at stopover sites in the<br />

Netherlands have led to a reduction in the number of Ruffs<br />

migrating through W Europe in favour of the E European<br />

route. Numbers on the West African wintering grounds have<br />

been stable; we therefore hypothesize that the European Ruff<br />

is becoming an Asian species.<br />

Prediction of suitable wader habitat in the<br />

British uplands using multiple spatial scales<br />

and aerial images<br />

Ute Bradter, Tim J. Thom, John D. Altringham,<br />

William E. Kunin & Tim G. Benton<br />

University of Leeds, UK; bsub@leeds.ac.uk<br />

Species-habitat models can predict suitable habitat for species<br />

and are thus an important tool in the conservation of<br />

vulnerable and declining species. Mobile species may select<br />

and use habitat at multiple spatial scales and bird-habitat<br />

relationships have frequently been found to depend on the<br />

scale of the investigation. Advances in geographic information<br />

systems (GIS) and in computer processor capacity make<br />

it increasingly possible to compute habitat variables at different<br />

spatial scales and to include larger scales. However, a<br />

major restriction of large-scale species-habitat models is the<br />

limited availability of landscape-scale habitat variables. We<br />

predicted 25 vegetation community classes for 1,939 km 2 of<br />

the Yorkshire Dales, UK, from reflectance values of colour<br />

aerial images and from environmental variables with an ensemble<br />

classifier. The selection of appropriate scales for this<br />

and other variables for inclusion in species-habitat models<br />

will be discussed. We will use the Eurasian Curlew Numenius<br />

arquata as an example.<br />

Energetic trade-offs of wintering<br />

at different locations in a migratory shorebird<br />

José A. Alves 1 , Tomas G. Gunnarsson 2,3 ,<br />

Daniel Hayhow 1 , Peter M. Potts 4 ,<br />

William J. Sutherland 5 & Jennifer A. Gill 1<br />

1 School of Biological Sciences, University of East Anglia,<br />

Norwich, NR4 7TJ, UK; j.alves@uea.ac.uk<br />

2 University of Iceland, South Iceland Research Centre,<br />

Tryggvagata 36, IS-800 Selfoss, Iceland<br />

3 Gunnarsholt, IS-851 Hella, Iceland<br />

4 Solent Court Cottage, Chilling Lane, Warsash,<br />

Southampton SO31 9HF, UK<br />

5 Department of Zoology, University of Cambridge,<br />

Downing St., Cambridge, CB2 3EJ, UK<br />

Migratory bird species often winter over large geographic<br />

and latitudinal ranges across which individuals encounter<br />

very different environmental conditions. If sites in different<br />

parts of the range vary in the quality of food resources and/<br />

or in weather conditions, the choice of winter location may<br />

strongly influence individual fitness. However, variation in<br />

the benefits associated with different winter sites may be<br />

traded-off with costs of migration and the timing of arrival<br />

on the breeding grounds. Icelandic Black-tailed Godwits<br />

Limosa limosa islandica, breed almost exclusively in Iceland,<br />

but their winter distribution ranges from Britain and Ireland<br />

to the Iberian Peninsula. Therefore individuals at different<br />

ends of the range are likely to experience very different<br />

environmental conditions. As godwits are highly site-faithful,<br />

the variation in conditions experienced at different winter<br />

sites may be a key driver of individual fitness. In this study,<br />

we calculate the net energetic benefits for Icelandic godwits<br />

wintering in three distinct parts of the range (England, Ireland<br />

and Portugal), by combining detailed measures of intake<br />

rates and time-budgets. We then estimate the energetic thermoregulatory<br />

costs (maintenance metabolism) for Icelandic<br />

godwits wintering in each site by adapting an energetic model<br />

developed for waders based on local weather variables. The<br />

potential trade-offs involved in winter site-choice are then<br />

explored by comparing the energetic benefits of each wintering<br />

site with migration distance, timing of arrival and annual<br />

survival of individually marked birds from each site.<br />

The relationship between social waders<br />

and their resource<br />

Eelke Folmer<br />

University of Groningen, CEES, Animal Ecology,<br />

the Netherlands; E.O.Folmer@rug.nl<br />

The ideal free distribution represents an equilibrium that<br />

emerges when all animals choose a location such that their<br />

fitness is maximized. When applied to foraging waders, it is<br />

typically assumed that suitability of a patch merely depends<br />

on food density and the level of interference. However, waders<br />

may also benefir from the co-occurence of conspecifics<br />

due to, for example, information sharing and to avoid predation.<br />

Thus, spatial aggregations of foraging waders are driven<br />

by a combination of attractive and repellent forces that are<br />

mediated by the environment. Due to the conspecific attraction,<br />

non-linear wader–benthos relationships emerge. The empirical<br />

challenge is to obtain statistical estimates that reflect<br />

the true impact of resource and to quantify the effect of social<br />

attraction. I will demonstrate by means of simulation what the<br />

consequences of social attraction may be. For this purpose,<br />

Beddington’s functional response model was generalized so<br />

that it allows for distant dependent conspecific facilitation.<br />

In this context I will also show how a population as a whole<br />

may benefit from individuals that are indifferent to conspecifics<br />

(i.e. leaders). Besides demonstrating the consequences<br />

of social attraction, I will show that spatial autoregressive<br />

(SAR) models are able to capture this effect. This provides<br />

opportunities for empirical investigations. Mudflats with<br />

foraging shorebirds provide a very good system to estimate<br />

the relationships between shorebirds and their benthic food<br />

while taking into account conspecific attraction. We mapped<br />

resource and wader densities across the Dutch Wadden Sea<br />

and applied SAR models to the relationships from which I<br />

will present and discuss the outcome.


218 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (1) 2009<br />

Conservation<br />

Two sides of the same story: threats to wader<br />

conservation and potential risks for air traffic due to<br />

the current plan for the new airport of Lisboa<br />

Pedro M. Lourenço 1 & José A. Alves 2<br />

1 Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies, University of Groningen,<br />

PO Box 14, 9750AA Haren, the Netherlands<br />

p.m.g.lourenco@gmail.com<br />

2 Centre for Ecology Evolution and Conservation,<br />

School of Biological Sciences,<br />

University of East Anglia, Norwich, NR4 7TJ, UK<br />

Most wader populations have very specific habitat requirements.<br />

During part of the year they are limited to a few<br />

relatively small areas of favourable habitat, making them<br />

extremely sensitive to human-induced habitat change. Continental<br />

Black-tailed Godwits Limosa limosa limosa use rice<br />

fields as their main foraging habitat in Portugal during the<br />

non-breeding season. In Jan and Feb, the rice fields near the<br />

Tejo estuary support as much as a third of the population<br />

during a long migration stopover. Currently, the Portuguese<br />

goverment is planning the construction of a new international<br />

airport for Lisboa which, when fully operational, will account<br />

for the majority of air traffic flying in and out of Portugal.<br />

The annouced location for this infrastructure is the Campo<br />

de Tiro de Alcochete, an old military base located on the<br />

south bank of the Tejo estuary. In this study, we evaluate two<br />

complementary aspects of the impact of the new airport. First,<br />

we consider the proximity of the airport site to important<br />

foraging and roosting sites used by Black-tailed Godwits and<br />

other waders, in an attempt to understand how such a large<br />

development might impact the local bird commmunity both<br />

in the rice fields and on the estuary. Second, we investigate<br />

how known flight patterns of Black-tailed Godwits between<br />

different rice fields and between estuarine roosts and ricefields<br />

might pose a serious threat for future air traffic.<br />

Building a user-friendly model<br />

to advise shorebird policy and management<br />

R.A. Stillman & A.D. West<br />

Bournemouth University, UK<br />

rstillman@bournemouth.ac.uk<br />

To assess the impact of future environmental change on<br />

shorebirds, conservationists, policy makers and developers<br />

require accurate predictions for new environmental conditions.<br />

The difficulty with this is that there will often be no<br />

historical data on which to base predictions, yet such data<br />

are usually required by traditional methods of prediction,<br />

such as regression or demographic models. In recent years,<br />

individual-based models (IBMs) have been developed to<br />

make such predictions of the effects of environmental change<br />

on shorebirds. These models predict the responses of populations<br />

to environmental change from the behavioural responses<br />

of the individual animals that comprise these populations.<br />

The decision making of model animals mimics that of real<br />

animals (e.g. model animals feed in the locations in which<br />

they can feed at a maximum rate), and so model animals<br />

are expected to respond to change in the same way that real<br />

animals would. These IBMs have been shown to accurately<br />

predict the responses of shorebird populations to change, and<br />

have been used in several estuaries to advise the management<br />

of shellfishing, disturbance, habitat loss and response to sea<br />

level rise. However, they have had the drawback that their use<br />

has been restricted to specialist modellers, whereas, ideally,<br />

they should be accessible to non-specialists with a direct interest<br />

in coastal management and policy. In this talk, we give a<br />

brief overview of these models and their application, and then<br />

describe a new user-friendly model that is being developed<br />

to allow coastal interest groups to use these models directly<br />

to assist their site management and policy. The new model<br />

allows a user to parameterise and run a model in a series of<br />

simple steps, and hides technical details (e.g. equations to<br />

predict energy requirements or feeding rate) from the user.<br />

We describe how the model is being tested in the UK by eight<br />

coastal interest groups, and how it will be made available in<br />

the future.<br />

<strong>Wader</strong>s of the Tagus rice fields<br />

N. Cidraes-Vieira<br />

Rua das Acácias 109, Gambelas, Faro, Portugal<br />

ncvieira@sapo.pt<br />

Rice fields are man-made wetlands of great importance for<br />

bird conservation. Although Portuguese rice fields are among<br />

the major rice growing regions of Europe, little is known<br />

about their use by birds. To study the bird communities of this<br />

habitat throughout the whole rice-cultivation cycle, counts<br />

were carried out at least once a month for three years. The<br />

area sampled includes the majority of the rice fields of the<br />

left bank of Tagus River and its tributaries, from Alcochete<br />

to Paul de Magos. The rice fields were observed from a car<br />

and scanned for birds using binoculars and telescopes. The<br />

phenology of the 22 wader species identified, their distribution<br />

and the importance of these rice fields to their conservation<br />

are analysed and discussed. The Tagus rice fields are<br />

used by >30,000 birds, mostly Black-tailed Godwits Limosa<br />

limosa, and should therefore be considered as an Important<br />

Bird Area, although most of them have no legal protection<br />

at the present time.<br />

Colonisation rates of waders in a<br />

newly created intertidal area:<br />

influence of biological and physical factors<br />

Lucas Mander, Krysia Mazik, Daryl Burdon & Nick Cutts<br />

Institute of Estuarine and Coastal Studies,<br />

University of Hull, Hull,UK; l.mander@hull.ac.uk<br />

The process of coastal squeeze, coupled with the long-term<br />

effects of climate change, has generated the need to create<br />

or restore intertidal habitats in estuaries. In the Humber<br />

Estuary (UK), 80 ha of mudflat was created in 2003 by<br />

breaching existing flood defences to allow tidal inundation,<br />

accretion and subsequent colonisation of the new intertidal<br />

habitat by foraging waders. To assess colonisation patterns<br />

and determine rates of change, monthly counts of waders<br />

have been undertaken since 2003 at the Paull Holme Strays<br />

managed realignment site. In parallel, benthic invertebrate<br />

and accretion monitoring have been undertaken since 2003<br />

218


Annual Conference<br />

219<br />

to determine the influence of biological and physical factors<br />

on the colonisation rates of several wader species. Six years<br />

after the initial breach of the sea-wall, the increase in foraging<br />

waders is attributed largely to the build-up of estuarine mud in<br />

the realignment site and associated development of the intertidal<br />

invertebrate community. Rates of colonisation however<br />

differed greatly between wader species and were found to be<br />

strongly linked to accretion rates, sediment types and benthic<br />

communities present within the realignment site. Although<br />

the ecological development of managed realignment sites<br />

has been well documented across the world, little has been<br />

presented on the colonisation process of wader species and<br />

their interactions with biological and physical factors. This<br />

has important implications for assessing the design and success<br />

of habitat creation for wader populations.<br />

Assignment of subspecies in wintering and<br />

migrating flocks of Black-tailed Godwits<br />

Limosa limosa<br />

Ricardo J. Lopes 1 , José A. Alves 2 , Jennifer A. Gill 2 ,<br />

Tómas G. Gunnarsson 3,4 , Jos C.E.W. Hooijmeijer 6 ,<br />

Pedro M. Lourenço 6 , Jose A. Masero 8 ,<br />

Theunis Piersma 6,7 , Peter M. Potts 5 &<br />

Francisco Santiago-Quesada 8<br />

1 CIBIO, Centro de Investigação em Biodiversidade e<br />

Recursos Genéticos, Campus Agrário de Vairão,<br />

4485-661 Vairão, Portugal; ricardolopes@mail.icav.up.pt<br />

2 Centre for Ecology Evolution and Conservation,<br />

School of Biological Sciences, University of East Anglia,<br />

Norwich, NR4 7TJ, UK<br />

3 University of Iceland, South Iceland Research Centre,<br />

Tryggvagata 36, IS-800 Selfoss, Iceland<br />

4 Gunnarsholt, IS-851 Hella, Iceland<br />

5 Solent Court Cottage, Chilling Lane, Warsash,<br />

Southampton SO31 9HF, UK<br />

6 Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies (CEES), University of Groningen,<br />

PO Box 14, 9750 AA Haren, the Netherlands<br />

7 Department of Marine Ecology, Royal Netherlands<br />

Institute for Sea Research (NIOZ), PO Box 59,<br />

1790 AB Den Burg, Texel, the Netherlands<br />

8 Conservation Biology Research <strong>Group</strong>, Zoology,<br />

University of Extremadura, Avenida de Elvas s/n,<br />

06071 Badajoz, Spain<br />

The location of wintering and migrating grounds of the different<br />

Black-tailed Godwit subspecies is crucial for an understanding<br />

of their dynamics. However, in sites where both subspecies<br />

occur, the relative importance of each can be difficult<br />

to estimate. Recent findings, analysing the control region of<br />

Mitochondrial DNA, show that there is geographic structure<br />

in the phylogeography of Black-tailed Godwits. L. l. limosa<br />

and L. l. islandica show clear discrimination of haplotypes,<br />

which are private for each subspecies. These results show<br />

that we can assign the subspecies of individuals caught on<br />

non-breeding grounds and clearly estimate the proportion of<br />

each subspecies in wintering and migrating flocks. We tested<br />

the previous findings and the accuracy of assignment before<br />

testing samples from wintering flocks. In the last decade, a<br />

large sample of birds from the two different subspecies that<br />

occur in W Europe were colour-ringed for individual identification.<br />

This was carried out at selected locations across their<br />

range, from breeding areas to wintering grounds and blood<br />

samples were taken from many of these birds. We selected<br />

all samples from Iberia during winter or pre-nuptial migration<br />

that allowed us to pinpoint the breeding location. All<br />

birds analysed were assigned correctly to each subspecies,<br />

confirming the accuracy of this approach. Then we tested<br />

>100 samples from birds caught in ricefields in SE Spain<br />

during winter and migration. Consistent with color-rings and<br />

morphological data, we discriminated several individuals of<br />

the islandica subspecies, but the proportion was


220 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

Social system and breeding biology of the<br />

Tuamotu Sandpiper Prosobonia cancellata<br />

Marie-Helene Burle 1 , David B. Lank 1 & Richard Lanctot 2<br />

1 Centre for Wildlife Ecology, Dept. of Biological Sciences,<br />

Simon Fraser University. 8888 University Drive, Burnaby,<br />

B.C. Canada V5A 1S6; msb2@sfu.ca<br />

2 U.S. Fish & Wildlife Service, Migratory Bird Management,<br />

Alaska, USA<br />

The Tuamotu Sandpiper Prosobonia cancellata is the last<br />

extant species of a poorly known radiation of tropical nonmigratory<br />

shorebirds of the South Pacific Ocean. Once<br />

widespread throughout the Tuamotu Archipelago (French<br />

Polynesia) and possibly beyond, the species is now restricted<br />

to four uninhabited atolls and is classified by the IUCN as<br />

endangered (www.iucnredlist.org). Reasons for the decline<br />

are introduced mammalian predators – primarily rats – and<br />

possibly habitat transformation through coconut plantations.<br />

Previous knowledge on distribution, abundance and presumed<br />

diet was summarized in 2004 by Pierce & Blanvillain (WSGB<br />

105: 93–100), but the social behaviour, communication<br />

system and breeding biology of this very peculiar species remained<br />

unstudied. Last winter we conducted a 5-month field<br />

season on the atoll of Tahanea, colour-banded and followed<br />

110 individuals and monitored 17 nests which produced 8<br />

chicks, the first to be described. Distribution among islets<br />

within Tahanea was very patchy – presumably reflecting the<br />

distribution of rats and suitable habitat – with most islets totally<br />

unoccupied, others holding a handful of birds and only<br />

five holding small but surprisingly dense breeding populations.<br />

On those, birds lived in pairs at very high densities<br />

in totally saturated habitat, on highly defended territories.<br />

Territories covered the entire area and non-territorial birds<br />

were chased away from one territory to another as soon as<br />

they were detected. Territorial birds also commonly engaged<br />

in sneaky foraging trips on other territories and were also<br />

chased when detected. The breeding season appeared to start<br />

in late December and continued beyond our departure in late<br />

March. Hatching success was low, apparently due to predation<br />

from unknown sources. Chicks had an unusually slow growth<br />

rate and fledging success was extremely low. We suggest that<br />

negative density-dependent reproductive success due to food<br />

competition may occur.<br />

Mating strategies of “faeder” male Ruffs<br />

Philomachus pugnax and inheritance of<br />

three male morph-types<br />

David B. Lank 1 , Susan B. McRae 2 & Lindsay L. Farrell 1<br />

1 Evolutionary and Behavioural Ecology Research <strong>Group</strong>,<br />

Simon Fraser University, 8888 University Drive,<br />

Burnaby BC V5A 1S6 Canada; dlank@sfu.ca<br />

2 Department of Biology, East Carolina University,<br />

Greensboro, NC, 27858, USA<br />

Jukema & Piersma (2006, Biology Letters 2: 161–164)<br />

discovered a rare “female mimic” morph of male Ruff, a<br />

lekking sandpiper previously known to have two genetically<br />

differentiated alternative male behavioural and morphological<br />

morphs, termed satellites and independents. The female-like<br />

“faeders” are smaller than ornamented males, lack ornamental<br />

plumage, and have large testes. We studied mimic behavior<br />

and inheritance patterns in a captive breeding colony. Two<br />

faeder males, sent by Piersma in 2006, produced 11 faeders<br />

out of 15 male offspring, and a faeder’s son produced 1 faeder<br />

of 2 sons. Most faeders do not perform recognizable male<br />

courtship displays, however two of 14 have done so. One<br />

briefly courted actively crouching females when a satellite<br />

male, but no independent was present. The second faeder<br />

essentially joined a lek, behaving somewhat like a satellite.<br />

Typically, however, faeders simply stand close to displaying<br />

males at leks, and may be courted by them. Faeders obtain<br />

copulations by responding quickly to crouching females,<br />

often inserting themselves between a crouching female and<br />

the attendant ornamented male. This does not suggest female<br />

choice for mating with the faeder. However, some females<br />

approached and spontaneously crouched to solicit matings<br />

from faeders, even when an ornamented male was available<br />

to them, suggesting both recognition of them as males and<br />

choice of them as mates. Faeders also crouch to distract or<br />

decoy other males away from mating with soliciting females.<br />

Pedigree data support a model of a simple Mendelian onelocus<br />

two-allele mode of inheritance, with a dominant allele<br />

producing a faeder. Epistatis is suggested, in that having a<br />

“faeder allele” overrides expression at the previously described<br />

“satellite-independent” locus determining development<br />

into the two types of ornamented males (Lank et al.<br />

1995, Nature 378: 59–62).<br />

Sexual differences in parental care of<br />

Upland Sandpipers<br />

Brett Sandercock<br />

Kansas State University, Division of Biology, 116 Ackhert<br />

Hall, 66506-4901 Manhattan, USA; bsanderc@ksi.edu<br />

The Upland Sandpipers is a poorly known species of shorebird<br />

that nests in the native grasslands of N America. As part<br />

of a long-term population study at Konza Prairie in NE Kansas,<br />

we investigated sexual differences in parental care of 51<br />

broods from successful nests in a 7-year period (2002–2008).<br />

Sandpipers were trapped at night using spot-lighting, individually<br />

marked with coloured leg bands, and a subset of birds<br />

was marked with radio-transmitters to locate nests. Birds<br />

were sexed with molecular methods applied to blood samples.<br />

Male and female Upland Sandpipers shared incubation but<br />

parental care of broods was primarily by males. A total of 24<br />

of 34 males (73%) but only 3 of 18 females (17%) attended<br />

broods after hatching of young. Parental sandpipers either<br />

abandoned broods shortly after hatching or attended broods<br />

for 2–4 weeks. Duration of parental care by males declined<br />

seasonally and was explained by date of hatching (r 2 = 0.2).<br />

Parental attendance of late-hatched broods was short, possibly<br />

because young were abandoned at earlier stages or because of<br />

seasonal increases in rates of brood failure. Overall, parental<br />

care in Upland Sandpipers was comparable to other socially<br />

monogamous shorebirds, suggesting that ecological factors<br />

determining sexual differences in brood attendance and timing<br />

of departure may be similar among temperate and arcticbreeding<br />

species.


Moult<br />

221<br />

Differing moult strategies of waders using<br />

freshwater habitats and coastal habitats<br />

of southern Africa<br />

Magdalena Remisiewicz 1,2 , Anthony J. Tree 3 ,<br />

Les G. Underhill 1 & P. Barry Taylor 4<br />

1 Animal Demography Unit, Department of Zoology,<br />

University of Cape Town, Rondebosch 7701,<br />

South Africa; biomr@ug.edu.pl<br />

2 Avian Ecophysiology Unit, Dept. of Vertebrate Ecology<br />

and Zoology, University of Gdańsk, al. Legionów 9,<br />

80-441 Gdańsk, Poland<br />

3 Zoology Dept., Nelson Mandela Metropole University,<br />

PO Box 1600, Port Elizabeth 6000, South Africa<br />

4 School of Biological and Conservation Sciences,<br />

University of KwaZulu-Natal, Private Bag X01,<br />

Scottsville 3209, Pietermaritzburg, South Africa<br />

According to hypotheses suggested by Prater (1981), the<br />

duration of moult in adult Palearctic migrant waders of<br />

northern temperate zones is correlated with their wing-length<br />

and with latitude, but these relationships break down in the<br />

southern hemisphere. We present an additional hypothesis:<br />

that moult strategy differs between waders using freshwater<br />

and coastal habitats, and verify the relationships suggested<br />

by Prater for waders moulting in sub-tropical Africa. We<br />

compared attributes of primary moult at similar latitudes in<br />

southern Africa for adults of nine Palearctic migrant waders:<br />

Wood Sandpipers, which exclusively use freshwater habitats;<br />

Common Sandpipers, Little Stints, Curlew Sandpipers and<br />

female Ruffs, which use freshwater or coastal habitats; and<br />

Red Knots, Sanderlings, Ruddy Turnstones and Grey Plovers,<br />

which use mostly coastal habitats. The moult parameters were<br />

estimated using the Underhill–Zucchini model (1988). We<br />

analysed 1,496 moult cards for Wood Sandpipers and 2,406<br />

moult cards for Little Stints; for the remaining species we<br />

used data from the literature. The correlation between winglength<br />

and the duration of primary moult was significant<br />

when we split these species into two groups: waders using<br />

coastal habitats and those using inland habitats, allocating<br />

Curlew Sandpiper to the inland group. The model, with two<br />

parallel lines fitted for the inland and coastal groups, showed<br />

that for each additional millimetre of wing length, the duration<br />

of primary moult was extended by half a day. Moult for<br />

inland waders lasted on average 25.9 days longer than for<br />

coastal waders. We consider the extended moult of waders<br />

using freshwater habitats to be an adaptation to their use of<br />

irregular wetlands that provide unpredictable food resources<br />

and to their need to move between ephemeral wetlands during<br />

the moulting period, in contrast to waders relying on the<br />

abundant and predictable food supplies of coastal habitats.<br />

Prolonged and flexible primary moult overlaps<br />

extensively with breeding in the Hooded Plover,<br />

a beach-nesting specialist<br />

Ken G. Rogers 1 , Michael A. Weston 2 & Danny I. Rogers 3<br />

1 340, Ninks Road, St Andrews, Victoria, 3761, Australia<br />

kenrogers@hotkey.net.au<br />

2 School of Life and Environmental Sciences,<br />

Faculty of Science and Technology, Deakin University,<br />

221 Burwood Hwy, Victoria, 3125, Australia<br />

3 Arthur Rylah Institute, PO Box 137, Heidelberg,<br />

Victoria 3084, Australia<br />

In general, the primary moult of birds is somewhat compressed<br />

in time, lasting less than about 5 months, and occurs<br />

after breeding. Very protracted moults, lasting longer than<br />

half a year, are traditionally considered to be restricted to<br />

very large species, or to some species living in unpredictable<br />

arid environments. In this study we demonstrate that none of<br />

these generalizations apply to the Hooded Plover Thinornis<br />

rubricollis, a resident of oceanic beaches of SE Australia.<br />

The relationship between breeding and adult primary feather<br />

moult was examined using data from a colour-banded population<br />

in which the breeding activity of all indivuals was<br />

known. Breeding and population moult cover long periods<br />

(approximately six and at least nine months respectively).<br />

Modelled durations of primary moult were long (sexes combined,<br />

203.3±9.05 [SE] days), and predictable that moult was<br />

centred on the austral summer and did not occur in winter.<br />

The population moult period entirely encompassed the breeding<br />

period, and many breeding birds were in active moult.<br />

All moult formulae fell on one of two moult sequences, one<br />

more rapid than the other. The slow sequence has fewer feathers<br />

growing concurrently and also has formulae indicating<br />

suspended moults. Switching between sequences can and<br />

does happen at many points in the moult cycle. A prolonged<br />

moult with the flexibility to move between sequences of<br />

“slower”and “faster” moult may facilitate high levels of<br />

replacement clutches associated with a high-risk nesting<br />

environment. Suspended moults may arise for several reasons<br />

including coping with extremes of temperature heat or<br />

disturbance in mid-summer, or perhaps the energetic demands<br />

of breeding or parental care.<br />

The effect of breeding success on the<br />

migration phenology and onset of moult<br />

of the Curlew Sandpiper Calidris ferruginea<br />

Yahkat Barshep & Les G. Underhill<br />

Animal Demography Unit, Department of Zoology,<br />

University of Cape Town, Rondebosch 7701, South Africa<br />

Yahkat.Barshep@uct.ac.za<br />

Fluctuations of breeding success in the Curlew Sandpiper<br />

results, primarily, from changes in predation pressure upon<br />

birds’ clutches (Summers et al. 1987), but sometimes temperature<br />

can contribute to the outcome of breeding as well<br />

(Schekkerman et al. 1998). The link between breeding success<br />

and the phenology of migration and moult in the Curlew<br />

Sandpiper was investigated using ringing data spanning 60<br />

years from Sweden and moult data from Australia. Results<br />

show that adults migrated earlier in years of poor breeding<br />

success (median date: 25 Jul) compared with years of good<br />

breeding success (median date: 5 Aug). There was also a link<br />

between the timing of migration and average June temperature<br />

in the arctic: birds migrated earlier in years when the<br />

average June temperature was cooler. The mean start date<br />

of moult in Australia was 15 Sep in poor breeding years and<br />

25 Sep in good breeding years. This study demonstrates the<br />

carry-over effect of events happening on the breeding ground<br />

on the schedule of migration and, subsequently, moult.<br />

221


222 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

Are Pacific Golden Plovers Pluvialis fulva<br />

distinguished in two subspecies<br />

Joop Jukema 1 , Jeroen Reneerkens 2 & Wally Johnson 3<br />

1 Haerdawei 62, 8854 AC Oosterbierum, Fryslân,<br />

the Netherlands; jukema42@hetnet.nl<br />

2<br />

Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies, University of Groningen,<br />

PO Box 14, 9750 AA Haren, the Netherlands;<br />

J.W.H.Reneerkens@rug.nl<br />

3<br />

Department of Ecology, Montana State University,<br />

Bozeman, Montana 59717, USA.<br />

owjohnson2105@aol.com<br />

Pacific Golden Plovers breed on the Arctic tundra. In N<br />

Siberia, the breeding area ranges from the Yamal Peninsula<br />

in the west to the Chukotskiy Peninsula in the east. Pacific<br />

Golden Plovers also breed in W Alaska. To date, no intraspecific<br />

population structuring within the Pacific Golden Plover<br />

has been reported. However, there are some indications that<br />

breeding birds in Siberia are shorter-winged than birds from<br />

W Alaska. This hints at population segregation, but the data<br />

set was limited and measurements were done by several<br />

different observers. The two putative breeding populations<br />

are geographically separated by the Bering Strait. This<br />

geographical barrier might have resulted in segregation in<br />

respect of other morphological and life-history characters. To<br />

further explore possible differences between the two putative<br />

populations, an analysis of the following characters will be<br />

presented based on museum skins and live birds: biometric<br />

measures, moult schedules and migratory connectivity with<br />

wintering areas.<br />

Population dynamics – Monitoring<br />

Breeding waders in the<br />

Middle Pripyat floodplain, S Belarus<br />

Pavel Pinchuk, Natalia Karlionova & Dmitriy Zhuravlev<br />

Institute of Zoology, NAS Belarus, 27 Academichnaya Str.,<br />

Minsk 220072, Belarus; ppinchuk@mail.ru<br />

The Pripyat floodplain contains the largest areas of natural<br />

meadows not only in Belarus, but in Europe. Large river floodplains<br />

are especially important for the conservation of breeding<br />

waders. During 2000–2008, we carried out counts of breeding<br />

waders on areas of the right bank of the floodplain from<br />

Stachovo village to Turov, and around the Stviga mouth near<br />

Pogost village and to the Pererovski Mlynok (total area about<br />

1,000 km 2 ). This study area includes both natural lowland<br />

and floodplain meadows. Part of the latter comprises unique<br />

floodplain, steppe-like meadows, with no analogous habitats<br />

in the rest of Belarus. Such steppe-like meadows support high<br />

breeding numbers of Eurasian Oystercatchers (25–40 pairs),<br />

Little Ringed Plover (10–30 pairs), Ringed Plover (200–250<br />

pairs – 80% of the Belarus breeding population), Northern<br />

Lapwing (550–800 pairs), Ruff (50–120 females), Common<br />

Snipe (100–250 pairs), Great Snipe (120–170 females), Blacktailed<br />

Godwit (300–500 pairs), Redshank (900–1250 pairs)<br />

Marsh Sandpiper (20–50 pairs) and Terek Sanpiper (100–150<br />

pairs – 60% of the Belarus breeding population). Data on the<br />

distribution, breeding density and breeding biology of waders<br />

were collected during Mar–Jun 2005–2008 on multiple plots<br />

of the meadow near Turov town (52.04°N, 27.44°E). The<br />

breeding density of waders varies across the breeding season<br />

and under a normal hydrological regime reaches a maximum<br />

(20–50 pairs/ha) at the end of April or beginning of May. But<br />

in very wet years (e.g. in spring 2008 when water levels rose to<br />

a high level, leading to a sharp decrease in the area of islands),<br />

breeding density can reach a maximum of 1,000 pairs/ha (60<br />

nests were found in 0.06 ha). Overall during 2005–2008, nest<br />

success of all studied species was 69.0–85.5%. Nest destruction<br />

might be explained by the grazing of horses and cows,<br />

predation by Corvids and Red Fox and inundation of nests in<br />

the 2008 flood. The main threats to breeding waders in this<br />

area are: changes in the hydrological regime, overgrowing of<br />

floodplain meadows by willow shrubs, managed burning the<br />

vegetation (affects early breeding species), high density of<br />

Corvids in the floodplain, uncontrolled cattle pasture, agricultural<br />

use of breeding habitats, spring hunting, disturbance by<br />

humans, destruction of nests by dogs and foxes, destruction of<br />

nests by local people. However, in spite of all these threats, the<br />

Pripyat floodplain remains an important breeding area for several<br />

wader species. If this status is to be maintained, it requires<br />

special protection and careful management.<br />

Results of ten years retrapping: Adults for Survival<br />

(RAS) project on breeding Redshanks<br />

Tringa totanus at Wieringen, the Netherlands<br />

Wim Tijsen 1 & Hans Schekkerman 2<br />

1 De Dolven 39, 1778 JP Westerland, the Netherlands<br />

wimtijsen@planet.nl<br />

2 Pernestraat 37, 1901 AV Castricum, the Netherlands<br />

hans.schekkerman@sovon.nl<br />

Between 2000 and 2009, we colour-ringed 203 breeding<br />

adult Redshank and 77 near-fledged juveniles in meadows<br />

along the Dutch Wadden Sea coast of North-Holland, and<br />

systematically resighted these birds to determine survival,<br />

pair bonds and breeding success. The study is conducted<br />

in two areas to determine if there is a difference in survival<br />

and reproductive success between nature reserve areas and<br />

farmland under agri-environment schemes. Catching methods<br />

used were a landing net and walk-in-traps. We used program<br />

MARK to estimate apparent survival and resighting rates.<br />

The best supported model included sex and age effects for<br />

resighting rate: p was 0.16 (95% CL 0.04–0.49) for 1st year<br />

birds, 0.86 (0.81–0.90) for adult females and 0.95 (0.91–0.98)<br />

for adult males. Apparent survival rate varied with age and<br />

year, with no discernible effect of transients. Average apparent<br />

survival rate was 0.24 (0.13–0.41) for first-year birds and 0.83<br />

(0.80–0.86) for adults, with annual values ranging from 0.74<br />

to 0.96. Adult Redshanks were highly faithful to their breeding<br />

territories. The average dispersal distance of recruiting<br />

juveniles was 2,123 m (range 82–9,660 m, n = 32); for young<br />

males this was 1,746 m (n = 19) and for females 2,713 m (n<br />

= 9). Mean duration of pair bonds was 3.24 years (n = 329<br />

years from 118 different pairs). Annually, 20% of all pairs<br />

dissolved because one partner did not return, 3% because<br />

both partners disappeared, and 10% through divorce, while<br />

67% reunited. 60% of divorces occurred after a year with<br />

hatching succes, while the mean overall hatching succes was


Annual Conference<br />

223<br />

43%, varying between years from 25.5% to 58.5% (n = 43–64<br />

nests). Experienced pairs raised their young more successfully.<br />

Chick survival can be improved by sympathetic mowing<br />

schedules and by creating wet-grassland-features. This study<br />

will be continued for the next ten years.<br />

Natal origin of breeding individuals affects<br />

estimates of local population growth rates<br />

Veli-Matti Pakanen, Kari Koivula, Antti Rönkä,<br />

Eduardo J. Belda, Aappo Luukkonen & Laura Kvist<br />

Department of Biology, University of Oulu, Finland<br />

veli-matti.pakanen@oulu.fi<br />

Vital rates of immigrants and philopatrics may differ due<br />

to different costs and benefits associated with dispersal and<br />

philopatry. Despite the apparent effects on population dynamics,<br />

immigration status is only rarely considered in analyses of<br />

population dynamics. We investigated whether immigration<br />

status causes variation in vital rates of an endangered Temminck’s<br />

Stint Calidris temminckii population breeding by the<br />

Baltic Sea. We also examined the impact of immigration and<br />

immigrant status on the population growth rate with a population<br />

matrix model in which immigrants and philopatrics represent<br />

their own states. Philopatric individuals survived better<br />

than immigrants. In reproductive parameters, variation due to<br />

immigrant status was not clear. Nest survival of philopatric’s<br />

nests was better than those of immigrants, but this did not show<br />

up in chick production per breeding attempt. Models described<br />

a sink population in which the inclusion of both immigration<br />

rate and the immigrant status of individuals into the model<br />

increased estimates of the population growth rate. When the<br />

better success of philopatrics was considered, the population<br />

appeared stable. If this was not taken into account, population<br />

growth was strongly negative. The results support the hypothesis<br />

that immigrants exhibit lower components of lifetime<br />

reproductive success and therefore contribute less to population<br />

growth and the gene pool than local recruits. While we cannot<br />

distinguish whether this difference reflects higher mortality or<br />

permanent emigration, the latter explanation seems more plausible.<br />

Our results demonstrate the importance of considering<br />

immigration and immigration status in population modelling.<br />

The results imply that management directed to improve local<br />

recruitment would be a profitable option.<br />

Barr al Hikman (Oman): a hotspot for migratory birds<br />

within the Middle East/East African flyway<br />

Jim de Fouw 1,2 & Raymond Klaassen 3<br />

1<br />

Bureau Waardenburg Ltd. Consultants for<br />

environment & ecology; Jimdefouw@gmail.com<br />

2<br />

Netherlands Institute of Ecology, P.O. Box 1299,<br />

3600 BG Maarssen, the Netherlands<br />

3<br />

Department of Ecology, Lund University,<br />

Ecology Building, 223 62 Lund, Sweden<br />

Barr al Hikman, a pristine coastal wetland in Oman (Middle<br />

East), is probably one of the world’s least-disturbed, tropical,<br />

intertidal ecosystems. The site is an important wintering area<br />

for migratory waders within the Middle East/East African Flyway<br />

(MEEAF). In winter, Barr al Hikman hosts long- distance<br />

migrants from Scandinavia (Broad-billed Sand piper), Siberia<br />

(Bar-tailed Godwit, Dunlin) and E Siberia (Great Knot), medium/short-distance<br />

migrants from central Asia (Redshank,<br />

Lesser Sandplover), as well as regional breeders (Crab Plover,<br />

Kentish Plover). We have studied the ecology of migratory<br />

waders wintering at Barr al Hikman during three consecutive<br />

winter seasons (2006/2007–2008/2009) . Our studies confirm<br />

that it is an important wintering area for an astonishing variety<br />

of wader species. In total, about 310,000 waders winter there.<br />

<strong>International</strong>ly important numbers were recorded for 18 species<br />

(wintering population >1% of flyway population, Delany<br />

et al. 2009). This diversity is unmatched for any other area in<br />

Africa and W Eurasia.<br />

An extensive benthic sampling program revealed that the<br />

site is very rich in small molluscs, dominated by the Lucinid<br />

bivalve Pillucina fischeriana. The densities of polychaetes<br />

were rather low, but small crustaceans (amphipods) were<br />

abundant. Also noteworthy was the high diversity and abundance<br />

of crabs, and many wader species were feeding on<br />

crabs. Crabs thus seem to be a key component of the Barr al<br />

Hikman ecosystem. Observations of foraging birds revealed<br />

that not many feed on the most abundant prey (molluscs), but<br />

that most take small prey with low energy values.<br />

Barr al Hikman should be considered one of the key sites<br />

within the MEEAF. Our studies are beginning to establish<br />

connectivity for various species between Barr al Hikman<br />

and breeding, stopover, and other wintering sites. This is<br />

especially valuable as very little is known about connections<br />

within the MEEAF. One key record was the observation of<br />

a Dunlin that had been colour-ringed on its breeding site in<br />

Taimyr; the first recovery from the wintering area for the<br />

centralis subspecies. Another was the capture of a Bar-tailed<br />

Godwit ringed 20 years before at Langebaan lagoon, South<br />

Africa. Our ringing studies have also revealed that most<br />

species are faithful to Barr al Hikman as their wintering site.<br />

The nearby island of Masirah, which can be considered as<br />

a part of the Barr al Hikman ecosystem, is not particularly<br />

important for wintering waders, as confirmed by a survey we<br />

have recently carried out. This is in contrast to the situation<br />

in autumn when the island hosts as many as 26,500 waders<br />

(Pomeroy 1980). The large seasonal differences in numbers at<br />

Barr al Hikman and Masirah makes us wonder how close the<br />

sites come to carrying capacity during migration and winter.<br />

And where do these birds come from Future expeditions<br />

and information from other winter and stopover sites in the<br />

MEEAF might unravel these questions.<br />

Population monitoring of subarctic waders on their<br />

breeding grounds in N Sweden<br />

Åke Lindström, M. Green & R. Ottvall<br />

Department of Ecology, Lund University, Ecology Building,<br />

S-223 62 Lund, Sweden; Ake.Lindstrom@zooekol.lu.se<br />

Generally, the population sizes, trends, and the geographical<br />

distribution of wader species breeding in northern tundra<br />

and taiga regions are poorly known. For N Sweden, which<br />

harbours large populations of several northern wader species,<br />

data on abundance have been scant. In 1996, a census scheme<br />

was launched that uses fixed routes, systematically distributed<br />

over the whole of Sweden. About 400 routes are situated in<br />

the northern taiga and tundra regions, many of them in rather<br />

inaccesible areas. We give an overview of wader monitoring<br />

in Sweden in general, and specifically what has been achieved<br />

so far by the fixed route scheme, including data on trends<br />

and distribution of several species, such as Eurasian Golden<br />

Plover, Whimbrel, Wood Sandpiper, Greenshank, Spotted<br />

Redshank and Ruff. We also discuss methodological aspects<br />

of monitoring breeding waders in the north.


224 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (1) 2009<br />

Abstracts of Conference Posters<br />

During the conference the Conference Coordinator, Jutta Leyrer, organised the usual poster competition and delegates voted<br />

for the one they preferred. The prizes were sponsored by CSIRO Publishing, Australia. The results were:<br />

First prize<br />

Black- tailed Godwits in Friesland: hatching success and agricultural land use by Elhacen Mohamed, Rosemarie Kentie,<br />

Pedro Lourenço & Theunis Piersma<br />

Second prize<br />

Crossbow-netting: a new method of catching waders by Ricardo C. Martins, Teresa Catry<br />

& José P. Granadeiro<br />

Third prize<br />

When will we encounter the first silent spring Predicting the fall of the Dutch Blacktailed<br />

Godwits by Julia Schroeder, Jos Hooijmeijer, Martin Hinsch & Theunis Piersma<br />

Fourth prize<br />

Analysis of Eurasian Stone-curlew Burhinus oedicnemus chick vocalizations by Chiara<br />

Caccamo, Dimitri Giunchi, Enrica Pollonara & Marco Dragonetti<br />

Elhacen Mohamed presenting the<br />

poster on “Black- tailed Godwits in<br />

Friesland: hatching success and<br />

agricultural land use” that won the<br />

poster competition. (Photo: Roos<br />

Kentie.)<br />

Right: The outdoor poster<br />

session. (Photo: Roos Kentie.)<br />

Predicting waterbird numbers at an estuary scale<br />

Aonghais Cook, Chris Thaxter,<br />

Graham Austin & Niall Burton<br />

Wetland and Marine Research Team, British Trust for<br />

Ornithology, The Nunnery, Thetford, Norfolk IP24 2PU, UK<br />

aonghais.cook@bto.org<br />

Estuarine waterbird densities are dependent on the abundance<br />

of their invertebrate prey, and thus in turn the nature of estuarine<br />

sediments, and so estuary morphology. Using data from<br />

the UK Wetland Bird Survey (WeBS), we developed models<br />

to predict waterbird densities from readily measured aspects<br />

of estuary morphology and climate.<br />

Analysis of Eurasian Stone-curlew<br />

Burhinus oedicnemus chick vocalizations<br />

Chiara Caccamo 1 , Dimitri Giunchi 1 ,<br />

Enrica Pollonara 1 & Marco Dragonetti 2<br />

1<br />

Department of Biology, Ethology Units, Pisa University,<br />

Via Volta 6, I-56126 Pisa, Italy; ccaccamo@biologia.unipi.it<br />

2<br />

Loc. Poderone, 58051 Magliano in Toscana (GR), Italy<br />

Vocal signals play a central role in all aspects of birds’<br />

social behaviour from cohesiveness within flocks to parent–<br />

offspring recognition. The latter is particularly important<br />

when the likelihood is high that parents and chicks might lose<br />

contact with one another or chicks might become attached to<br />

the wrong adults (e.g. in colonial species, and those that produce<br />

precocial chicks) and/or when the use of other signals,<br />

such as visual ones, is problematic (e.g. at night). Individual<br />

offspring vocal recognition requires (1) that the candidate<br />

signal is highly variable among individuals and (2) that parents<br />

can make use of that variability to recognize their own<br />

chicks. In this study we present the first analysis of Eurasian<br />

Stone-curlew chick vocalizations. Data were collected in the<br />

Taro River Regional Park (Parma, Italy). We hypothesized<br />

that in this population parent–offspring recognition could<br />

be particularly important because in this area breeding territories<br />

are densely packed (


Annual Conference<br />

225<br />

analysis. The resulting spectrograms showed at least four different<br />

call types: (1) a brief strangled sound with a broadband<br />

spectrogram, uttered mainly by younger chicks; (2) a short<br />

whistle preceded and/or followed by a strangled sound with<br />

a broadband spectrogram; (3) a drawn-out hissing sound followed<br />

or preceded by a yelping loud whistle (this last call was<br />

recorded by a chick in a distressed condition); (4) a loud short<br />

whistle with a complex morphology often uttered by older<br />

chicks, characterized by harmonic components and frequency<br />

modulation. This last call could be individually distinctive,<br />

but quantitative analysis of spectrograms and playback experiments<br />

are needed to assess whether it is actually used for<br />

individual recognition.<br />

Variation in growth rates of Piping Plover<br />

Charadrius melodus chicks on the Missouri River<br />

Daniel H. Catlin, Joy H. Felio,<br />

Jonathan B. Cohen & James D. Fraser<br />

Department of Fisheries and Wildlife Sciences,<br />

Virginia Polytechnic Institute and State University,<br />

Blacksburg, Virginia, USA; dcatlin@vt.edu<br />

Avian growth rates may be positively correlated with survival,<br />

but growth rate can be affected by individual, territory,<br />

or habitat quality. We studied the variation of growth<br />

rates at several hierarchical levels to determine where the<br />

greatest amount of variation was present in the growth of<br />

Piping Plover chicks on natural and engineered sandbars on<br />

the Missouri River. We captured, banded, and measured the<br />

mass (0.1 g), wing-chord (1 mm), and culmen (1 mm) of<br />

newly hatched piping plover chicks using sandbar habitat<br />

from 2005 to 2007. We continued to recapture and measure<br />

chicks until they were fledged or dead. We also evaluated<br />

the effect of habitat-type (natural vs. engineered sandbars),<br />

timing of hatch, and availability of foraging habitat (ha of<br />

moist habitat). We used a multi-level random effects model<br />

with sandbar, nest, and individual as levels of random variation.<br />

We modeled these effects for each of the morphometric<br />

measurements. Variation was greatest at the sandbar level,<br />

intermediate at the nest level, and least at the individual level.<br />

Birds that hatched earlier in the season and that had more<br />

foraging habitat available to them grew more quickly than<br />

others. Our results indicate that habitat recovery programs<br />

should not only focus on creating the appropriate amount of<br />

nesting habitat, but also on the amount of foraging habitat<br />

that is available and that this type of management should be<br />

directed at the sandbar level to take advantage of the greatest<br />

amount of variation in growth.<br />

Distribution and habitat use patterns of several<br />

waterbird species on tidal flats<br />

in the German Wadden Sea<br />

Pauline Dierichsweiler, Franziska Güpner,<br />

Philipp Schwemmer & Stefan Garthe<br />

Research and Technology Centre, University of Kiel,<br />

Hafentörn 1, 25761 Büsum, Germany<br />

dierichsweiler@ftz-west.uni-kiel.de<br />

The Wadden Sea is of great importance for breeding and<br />

migratory waterbirds. During low tide, the tidal flats provide<br />

important feeding grounds. In recent years, monitoring of<br />

birds at high tide roosts has revealed population declines<br />

in several (breeding and non-breeding) wader species (e.g.<br />

Haematopus ostralegus and Calidris canutus) in at least some<br />

parts of the <strong>International</strong> Wadden Sea. Currently, the reasons<br />

for these population declines are poorly known. However,<br />

changing conditions in the foraging habitats is a potentially<br />

important factor; therefore it is desirable to carry out analyses<br />

of habitat use. Although Wadden Sea birds are already well<br />

monitored by high tide roost counts and in their breeding<br />

habitats, knowledge of the foraging habitat use and their<br />

distribution on the mudflats is poor. In order to assess distribution<br />

patterns of various waterbird species on the tidal flats, we<br />

used low-tide, ship-based surveys to count foraging and resting<br />

waders, gulls and other non-foraging (resting) waterbirds.<br />

Habitat use patterns of species of dominant abundance were<br />

our main interest. Particularly, we focused on the distribution<br />

of the most abundant waders in comparison to gulls sharing<br />

the same habitat. Correlations between bird distribution and<br />

environmental data for the area (such as topography and sediment)<br />

were studied. Ship-based surveys started in selected<br />

parts of the German Wadden Sea of Schleswig-Holstein in<br />

2008 and are planned to be conducted regularly in the future.<br />

The poster will present preliminary results.<br />

Red Knot spring stopover in Virginia<br />

James D. Fraser 1 , Jonathan B. Cohen 1 ,<br />

Sarah M. Karpanty 1 , Barry R. Truitt 2 & Bryan D. Watts 3<br />

1<br />

Department of Fisheries and Wildlife Sciences, Virginia<br />

Polytechnic Institute and State University,<br />

Blacksburg, Virginia, USA; fraser@vt.edu<br />

2<br />

Virginia Coast Reserve, The Nature Conservancy,<br />

Virginia, USA<br />

3<br />

Center for Conservation Biology,<br />

College of William and Mary, Williamsburg, Virginia, USA<br />

Delaware Bay has received much attention as a stopover for<br />

northward migrating West Atlantic Flyway Red Knots Calidris<br />

canutus rufa and food shortage in the Delaware Bay has<br />

been blamed for a Red Knot population decline. Alternative<br />

stopover sites have received little study. Historical literature<br />

suggests a substantial stopover in Virginia, less than 200 km<br />

south of the Delaware Bay, as well as on Long Island, New<br />

York (200 km northeast of Delaware Bay), and Cape Cod,<br />

Massachusetts (500 km northeast of Delaware Bay). In<br />

2006–2008, we examined Red Knot numbers and turnover<br />

during the spring stopover in Virginia. Estimated stopover<br />

population, accounting for turnover, was 7,224, 8,332, and<br />

12,167 in 2006, 2007, and 2008 respectively. Fewer than 5%<br />

of radio-tagged birds were relocated in the Delaware Bay<br />

region in the tagging year, and those only at the end of the<br />

stopover season, suggesting that most birds in Virginia by 20<br />

May did most of their premigratory fattening there. The coast<br />

of Virginia consists of barrier islands backed by extensive<br />

marshes, similar to habitats used in the 19th century.<br />

Functional morphology of the<br />

feeding apparatus of snipes<br />

Kyrill B. Gerasimov<br />

Moscow Lomonosov State University, Biological faculty,<br />

Vertebrate zoology department, 119991, Vorobievy Gory,<br />

Moscow, Russia; gerasimov.kyrill@gmail.com<br />

This study investigated the feeding apparatus (including the<br />

form of the bill, the papillae on the palatal surface, the bill-tip


226 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

organ and the salivary gland) of Limnodromus scolopaceus,<br />

Lymnocryptes minimus, Gallinago gallinago, G. stenura,<br />

G. hardwickii, G. megala, G. solitaria, G. media, Scolopax<br />

rusticola and S. minor. If we orientate a skull of Scolopacinae<br />

in a natural position, with the jugal bars in a horizontal plane<br />

and the bill inclined downwards, it appears likely that the<br />

eye would have been pressed back (along the bill axis) and<br />

upwards by the base of the upper mandible. Besides of the<br />

ability to open the bill within a substrate (as widely discussed<br />

in the literature), an ability to withdraw an object (food) from<br />

the substrate is characteristic of the jaw apparatus of snipes.<br />

This is made possible by: (1) the separated muscular control<br />

of the jaws achieved by reduction of an external jugomandibular<br />

ligament, (2) the inclination of the bill downwards<br />

(clinorhynchy) (3) the increase in the length of the upper jaw,<br />

maintaining the length of the lower jaw, (4) distal rhynchokinesis,<br />

(5) a notable hypertrophy of the premaxillar process of<br />

nasale (which fastens the basal 2/3rds of the bill ridge). The<br />

snipes (and others probing waders) have no ability to lower<br />

the end of the lower jaw. Specializations of the species are<br />

interpreted on the basis of morphological data as follows:<br />

G. gallinago and especially Limnodromus scolopaceus and<br />

Lymnocryptes minimus are specialized for obtaining small<br />

prey from benthic mud; the first two species (G. gallinago<br />

and L. scolopaceus) do this from a considerable depth, but the<br />

latter two L. scolopaceus and L. minimus are partly specialized<br />

for feeding on surface-dwelling invertebrates (including<br />

flying insects). G. media, G. megala and S. rusticola<br />

are specialized for feeding on large prey taken from dense<br />

substrates, and S. rusticola also feeds in drier habitats. The<br />

imago of insects which are extracted exclusively by touch<br />

during probing of leaf litter probably play a significant role in<br />

the diet of Scolopax. S. minor is primarily specialized for this<br />

type of feeding. G. hardwickii and G. solitaria are probably<br />

specialized for extracting prey from rather dense substrates as<br />

well as from deep benthic mud. Five specimens of G. stenura<br />

that have been studied show significant differences in the relative<br />

ridge length of the upper mandible and in the orientation<br />

of the palatal papillae. Apparently, this species is similar in<br />

its specialization to G. media and G. megala. Yamal populations<br />

of G. stenura appear to be in the process of specializing<br />

almost exclusively on large underground prey, often taken<br />

from tussocks of cereals or sedges.<br />

New explanation of distal rhynchokinesis<br />

Kyrill B. Gerasimov<br />

Moscow Lomonosov State University, Biological faculty,<br />

Vertebrate zoology department, 119991, Vorobievy Gory,<br />

Moscow, Russia; gerasimov.kyrill@gmail.com<br />

We studied feeding apparatus in species of the genus Tringa<br />

(T. ochropus, T. glareola, T. totanus, T. erythropus, T. stagnatilis,<br />

T. nebularia), Heteroscelus (H. incanus, H. brevipes),<br />

Actitis hypoleucos and Xenus cinereus. In Spotted Redshank,<br />

the flexible zones in the upper mandible are situated at its<br />

base; in Wood Sandpiper, Common Sandpiper, and Terek<br />

Sandpiper near the end and in the rest they occupy different<br />

intermediate positions. It is repeatedly pointed out in the<br />

literature that birds with a rhynchokinetic upper mandible<br />

can take and squeeze prey using the flexibility of the end<br />

of the upper mandible alone, without having to use the jaw.<br />

This is why localization of the flexible zones nearer to base<br />

of the bill allow the taking of prey by the larger part of the<br />

bill rather than just the tip. This is probably useful for catching<br />

prey from water. On the other hand, if the flexible zones<br />

are near the tip, this would enhance the ability to open that<br />

part of the bill while probing. However, the tringini sandpipers<br />

with distal rhynchokinesis have moderately developed<br />

musculature for opening the bill. Therefore it is a means of<br />

overcoming an inability to open the bill. If retraction force<br />

is constant then the shift of flexible zones to the tip of the<br />

upper mandible increases the grip between the prey and<br />

the adductional components of the dorsal adductors. This is<br />

one of the reasons that the dorsal adductors of Scolopacinae<br />

have a large adductional component. Common and Terek<br />

Sandpiper do not have an external jugomandibular ligament,<br />

therefore their m. pterygoideus is capable of squeezing the<br />

upper jaw independently from the retraction component of<br />

the dorsal adductors. The flexible zones are situated nearer to<br />

the base of the upper mandible in the larger, stronger tringini<br />

sandpipers which have more forceful jaws. In the smaller,<br />

weaker species the flexible zones are situated near to the tip<br />

of the upper mandible. The Willet Catoptrophorus semipalmatus<br />

is the single exception to this rule, but it may be close<br />

in adaptation to Limosa species. The conclusion that distal<br />

rhynchokinesis in Scolopacidae appears to be for “feeding<br />

on small prey items suspended in water” (since Calidrinae do<br />

successfully feed this way (Estrella, Masero 2007)), is akin<br />

to the conclusion that the hand of a human appears to write<br />

with a pen. Moreover Phalaropinae, which are mostly adapted<br />

for feeding from water, has flexible zones in the middle of<br />

the upper mandible, while their ancestors seem to have distal<br />

rhynchokinesis (Gerasimov 2007, Kozlova 1961).<br />

Functional morphology of the feeding apparatus of<br />

Red Knot Calidris canutus,<br />

Great Knot C. tenuirostris and<br />

Surfbird Aphriza virgata<br />

Kyrill B. Gerasimov<br />

Moscow Lomonosov State University, Biological faculty,<br />

Vertebrate zoology department, 119991, Vorobievy Gory,<br />

Moscow, Russia; gerasimov.kyrill@gmail.com<br />

The Red Knot, Great Knot and Surfbird probably form a<br />

monophyletic group of birds, which is assumed to have<br />

separated from the Calidrinae during the initial evolution of<br />

this subfamily (Jehl 1968, Tomkovich 1985). Calidrinae’s key<br />

feeding adaptations are: detecting prey in substrate, pulling<br />

out food items from soft substrate, and feeding on surfacedwelling<br />

invertebrates (including flying insects) (Bolze 1968,<br />

Kozlova 1961, Taldenkov, Gerasimov 2006). To describe the<br />

specialization of these three species, we dissected their feeding<br />

apparatus. Unlike other Calidrinae species, Surfbird has a<br />

relatively more robust bill and strengthened adductory effect<br />

of the external adductor muscle (by an increase in the typical<br />

part of m.adductor mandibulae externus profundus rostralis).<br />

The bill of this species is relatively high and short. Also (for<br />

Calidrinae) it has a thick rhamphotheca and connective tissue<br />

underneath. The pits of the bill-tip organ are relatively large,<br />

with thick walls, but the number of pits is less than in the other<br />

two species. As a result, the bill-tip organ is less capable of<br />

locating sources of vibration than those of other Calidrinae.<br />

All these features are probably a result of adaptation of the<br />

Surfbird to collecting openly-lying, attached food-items on<br />

rocky shores (such as mussels, etc.) and to feeding on prey<br />

that has to be opened by pecking (such as barnacles). Knots


Annual Conference<br />

227<br />

have a more typical Calidrinae feeding apparatus structure.<br />

The Great Knot’s m. depressor mandibulae is increased, and<br />

its bill-tip organ has a thick rhamphotheca, as in Surfbird.<br />

Among these three species, the Great Knot’s bill-tip organ<br />

is the smallest in height and width. Great Knot seems to<br />

be adapted for collecting prey from relatively deep in soft<br />

substrates. The Great Knot searches by sensing vibrations<br />

made by its prey (mollusks, worms, tipulid larvae, etc.).<br />

The bill-tip organ of the Red Knot is the largest among the<br />

three species. The number of pits is the same or fewer than<br />

in typical Calidris but more than in Great Knot and Surfbird.<br />

The rhamphotheca is thin. The bill of the Red Knot is shorter<br />

than in Calidris of the same size, and the jaw musculature is<br />

the weakest among the three species. Red Knots probably<br />

collect most food items only from a shallow depth, including<br />

tiny and slow-moving creatures. Perhaps these facts are<br />

related to the fact that the Red Knot is able to feed in shallow<br />

thawed sod in the High Arctic at times when insects are rare<br />

and slow moving in low temperature conditions. As a result,<br />

Red Knot can only spend winter in locations with numerous<br />

and not-so-deep prey. The relatively large size of all three<br />

species reflects their initial adaptation to feeding on shellfish.<br />

Bivalves in muddy tidal flats at Meldorfer Bucht –<br />

a prey worthwhile for waders<br />

Franziska Güpner, Philipp Schwemmer & Stefan Garthe<br />

Research and Technology Centre, University of Kiel,<br />

Hafentörn 1, 25761 Büsum, Germany;<br />

guepner@ftz-west.uni-kiel.de<br />

The Wadden Sea is an important staging and moulting area for<br />

numerous waterbirds. Many migrant species use the Wadden<br />

Sea to refuel their energy stores before continuing their flight<br />

to Arctic breeding or southern wintering sites. Despite the<br />

well-established high conservation status of the Wadden Sea,<br />

the populations of many species have been declining at an<br />

alarming rate during recent years. Climate change, economic<br />

pressure in Arctic or African habitats, disturbance of water<br />

birds and changes in food resources are possible reasons for<br />

negative trends.<br />

The present study investigates the food resources (with<br />

a focus on bivalves) in particularly muddy tidal flats adjacent<br />

to the sea-dike in the sheltered bay of Meldorfer Bucht<br />

in the Schleswig-Holstein Wadden Sea. Common Cockle<br />

Cerastoderma edule and Baltic Tellin Macoma balthica, two<br />

important prey species for waders, were studied in detail:<br />

The density of the bivalves were determined by taking cores<br />

from 120 sampling stations during low tide from Oct to Dec<br />

2007. The size, biomass and quality of the bivalves was<br />

analysed and compared with the results of previous studies<br />

in the Schleswig-Holstein Wadden Sea. Finally, the results of<br />

the benthic studies were related to the presence and foraging<br />

behaviour of waders in the study area.<br />

The study shows the importance of muddy sediments<br />

adjacent to the coast with high abundance of benthic invertebrates<br />

as foraging sites for several waterbird species.<br />

Sea-level rise is expected to affect such sites in many parts<br />

of the Wadden Sea.<br />

Fluctuations in numbers of<br />

young Ruffs Philomachus pugnax during<br />

spring migration in the Pripyat Valley, Belarus<br />

Natalia Karlionova & Pavel Pinchuk<br />

Institute of Zoology, NAS Belarus, 27 Academichnaya Str.,<br />

Minsk 220072, Belarus; Karlionova@tut.by<br />

Studies of the spring migration of Ruffs through the floodplain<br />

meadows of the Pripyat Valley near Turov town, Belarus<br />

(Gomel Region, 52.04°N, 27.44°E) were carried out from<br />

2002 to 2009. This area is an important stopover site for<br />

waders during spring and autumn migration. Ruff is the most<br />

numerous wader species with the highest spring concentrations<br />

reached 10,000–14,000 birds around the end of April<br />

and beginning of May. Ruffs were captured in walk-in traps<br />

and mist-nets. 5,956 Ruffs were ringed during 2002–2009<br />

(3,384 males and 2,572 females). The proportion of young<br />

males varied between years from 8.4% to 19.0% and females<br />

from 4.7% to 11.9%. The mean proportion of young males<br />

(11.1%) was significantly higher than young females (7.2%)<br />

(Mann–Whitney U-test: Z = 2.20, p = 0.02). However, the<br />

yearly proportions of young birds of each sex were highly<br />

correlated (R-sq = 0.79; p = 0.003). We propose two hypotheses<br />

for such correlation: (1) the proportion of second-year<br />

birds depends on the breeding conditions during the previous<br />

nesting season and (2) the proportion of second-year birds<br />

depends on the conditions on the wintering grounds.<br />

Assessing the value of a newly-created mudflat on<br />

the Humber estuary, UK, through the study of<br />

foraging behaviour of Redshank Tringa totanus<br />

L. Marie-Orléach & L. Mander<br />

Institute of Estuarine and Coastal Studies.University of Hull,<br />

Hull, HU6 7RX, UK; lucas.marie-orleach@wanadoo.fr<br />

Rapid loss of intertidal habitat has resulted in the need to create<br />

new mudflats and sandflats in order to preserve waterbird<br />

populations. Although several studies have assessed the success<br />

of new intertidal habitats for waterbirds, a few studies<br />

have focused on the behaviour of waterbirds, in particular the<br />

foraging behaviour of benthivorous species. In order to assess<br />

the value of a newly created mudflat on the Humber Estuary,<br />

UK, counts of benthivorous species and focal observations<br />

of Redshank were undertaken on a newly-created mudflat<br />

(realignment site) and on an adjacent natural mudflat in<br />

April 2008. The abundance of benthivorous species in the<br />

realignment site was found to vary with the tides. Redshanks<br />

showed no significant differences in pecking and probing<br />

rates between the newly created mudflat and the natural<br />

mudflat. However, Redshank prey intake and success rate<br />

were lower in the managed realignment site: mean success<br />

rate of 25%±3 and 38%±7 were observed respectively in the<br />

newly-created mudflat and in the natural mudflat. Success<br />

rates were found to fluctuate according to the tidal cycle.<br />

Pace-rate was higher on the newly-created mudflat than on<br />

the natural mudflat. The discrepancy in foraging behaviour<br />

between the two areas might reflect the lower abundance and<br />

biomass of the invertebrate community in the realignment<br />

site. Furthermore, it could indicate that the newly created<br />

mudflat has not yet reached maturity.


228 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

Crossbow-netting: a new method of catching waders<br />

Ricardo C. Martins, Teresa Catry & José P. Granadeiro<br />

Centro de Biologia Ambiental,<br />

Museu Nacional de História Natural, Universidade de<br />

Lisboa, Rua da Escola Politécnica, 58.1269-102 Lisboa,<br />

Portugal; ricjmartins@hotmail.com<br />

Catching birds is very often an essential component in wader<br />

research, for instance for colour-ringing, radio-tracking, or to<br />

collect individual physiological and biometric data. Cannonnetting<br />

provides a solution for catching large number of<br />

waders, traditionally when they are concentrated at roosts.<br />

However, in many countries the use of cannon-nets can be<br />

quite difficult, because handling and transporting gunpowder<br />

requires rather strict police permissions, which can be difficult<br />

to obtain. We describe the use of a crossbow as a way<br />

of pulling a modified mist-net to capture waders in high-tide<br />

roosts. This system is similar to cannon-netting, differing only<br />

in the means by which the net is pulled. The main advantages<br />

in relation to cannon-netting include simpler logistics and setting<br />

up procedures and the lack of explosive materials, while<br />

the major limitation is a comparatively smaller catching area.<br />

A highly-trained and fine-tuned team is obviously of utmost<br />

importance. In this new method, a crossbow is used as the<br />

propulsion tool that shoots a heavy arrow attached to an edge<br />

of a net. The net opens quickly over the roosting flock. The<br />

net should be set during low-tide, when birds are dispersed<br />

in foraging areas. Camouflage of the apparatus is crucial to<br />

ensure that birds do not avoid the catching area. Wind speed<br />

and direction is much more important than in cannon-netting,<br />

because the net is very light and the power of the crossbow<br />

is much less than that provided by cannons. To avoid disturbing<br />

the birds, the crossbow can be triggered at distance<br />

(>100 m) using a customized remote control setup. Despite<br />

the relatively small size of the net used to date (38 m 2 ) and<br />

its shape (trapezium), the method has proved to be effective<br />

for catching small waders, with peak catches of about 100<br />

Dunlins in a single shot. It might be possible to achieve larger<br />

catches using a larger net and two synchronised crossbows.<br />

Overwintering ecology of White-rumped Sandpiper<br />

calidris fuscicollis at the southern limit of its range<br />

J.A. Masero 1 , J.M. Sanchez-Guzman 1 , A. Villegas 1 ,<br />

G. Escudero 2 , M. Castro 3 , A. Barbosa 4 , C.G. Suazo 5 ,<br />

R. Morán 1 , C. Corbacho 1 & J.S. Gutierrez 1<br />

1<br />

Grupo de Investigación en Biología de la Conservación,<br />

Área de Zoología, Universidad de Extremadura, Badajoz,<br />

Spain; jamasero@unex.es<br />

2<br />

Centro Nacional Patagónico, Puerto Madryn,<br />

Chubut, Argentina<br />

3<br />

Departamento Evaluación y Conservación de la<br />

Biodiversidad, Centro de Investigación de Ecosistemas<br />

de la Patagonia, Coyhaique, Chile<br />

4<br />

Departamento de Ecología Funcional y Evolutiva,<br />

Estación Experimental de Zonas Áridas,<br />

CSIC, Almería, Spain<br />

5<br />

Programa de Educación e Investigación Biológica y<br />

Ambiental (Programa IBAM), Universidad de Los Lagos,<br />

Osorno, Chile<br />

Despite the obvious importance of information on overwintering<br />

ecology to understand the life histories of many<br />

Nearctic shorebird species, there have been few formal<br />

studies at the southern limit of their ranges. An international<br />

research project started in 2008 with the aim of studying<br />

several aspects of the overwintering ecology of these Nearctic<br />

shorebird species in Tierra del Fuego, South America. Here,<br />

we show preliminary results on sex-ratio and the health and<br />

body condition of overwintering White-rumped Sandpipers<br />

at Bahía Lomas, Chile, (BL) and Bahía San Sebastián,<br />

Argentina, (BSS). Both bays are located at the southern range<br />

limit of this small-sized shorebird, supporting about 22% of<br />

the total population. Overall, sex-ratio was female-biased in<br />

both bays (BSS 69.4% females, BL 66.7% females). Whiterumped<br />

Sandpipers showed a very low ectoparasite load, and<br />

ectoparasite prevalence did not differ between sites or sexes.<br />

Molecular methods did not detect avian influenza or Newcastle<br />

disease in any of the birds sampled. Birds at BSS had<br />

higher size-corrected body mass and total white cell counts<br />

than BL birds, both variables being higher for females than<br />

males. Plasma levels of tryglicerides were higher in BSS and<br />

plasma glycerol levels were higher in BL. Our results suggest<br />

that habitat quality in Bahía San Sebastián may be better for<br />

small-sized migratory shorebirds than in Bahía Lomas.<br />

Some aspects of the bird fauna of Kosovo<br />

Qenan Maxhuni<br />

Ministry of Environment and Spatial Planning,<br />

Kosovo Environmental Protection Agency,<br />

Str. Bill Clinton No. 18, 10090 Pristine, Kosovo<br />

qmaxhuni@yahoo.com<br />

Kosovo has central geographical position in the Balkan Peninsula.<br />

It covers an area of 10,887 km 2 . Climate conditions,<br />

hydrological and geological factors etc, have led to a diversity<br />

of habitats and ecosystems and the development of a rich flora<br />

and fauna. Due to this richness, Kosovo is recognised as an<br />

area of great biodiversity, not only in Balkans but also in the<br />

wider world. The parts of Kosovo with the richest fauna are<br />

the mountainous massifs, the Sharr Mountains and Bjeshket<br />

e Nemuna, as well as river valleys and lakes.<br />

The fauna of Kosovo in general and the avifauna in particular<br />

are not well researched, but available information,<br />

indicates that the country supports over 200 bird species.<br />

Among the most important bird populations are those of<br />

Aquila chrysaetos, Falco naummani, Tetrao urogallus,<br />

Ardeola raloides, Ciconia ciconia, Ardea cinerea, Ixobrychus<br />

minutes and Tringa nebularia.<br />

Effects of farm management<br />

on breeding wader food resources<br />

Heather M. McCallum 1 , Jeremy Wilson 1,2 ,<br />

Robert D. Sheldon 2 , Mark O’Brien 2 , David Beaumont 2 ,<br />

Dave Gouslon 1 & Kirsty J. Park 1<br />

1<br />

University of Stirling, Stirling, Scotland, UK<br />

h.m.mccallum@stir.ac.uk<br />

2<br />

RSPB Scotland, UK<br />

Many changes in farming practices associated with agricultural<br />

intensification have been linked to declines in farmland<br />

breeding wader populations. This project investigates land<br />

management techniques currently employed at an upland<br />

livestock farm in Stirlingshire, Scotland, which appear to be<br />

associated with unusually high densities of breeding waders,<br />

in particular Northern Lapwing. Management involves cultivation<br />

of a forage brassica (tyfon), which is rotated round the


Annual Conference<br />

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farm. At the time of tyfon cultivation, the ground is enriched<br />

with lime and fertiliser. In order to assess the effect of land<br />

management (tillage, crop-type, lime and fertiliser) on factors<br />

important for breeding waders (food supply, vegetation<br />

structure) an agricultural field trial has been established with<br />

five different treatment types. Preliminary results indicate a<br />

higher proportion of bare ground and more penetrable soil<br />

within the tyfon treatment than in the non-tilled treatments,<br />

both of which are likely to be of benefit to breeding waders.<br />

However, during the first year of the trial the number of soil<br />

invertebrates within the tyfon treatment was found to be<br />

lower than with alternative management. Future work at the<br />

Stirling site, and at additional sites in Cumbria and on Islay<br />

will investigate habitat use by breeding waders and link this<br />

to food supply and vegetation structure.<br />

Black- tailed Godwits in Friesland:<br />

hatching success and agricultural land use<br />

Elhacen Mohamed 1 , Rosemarie Kentie 1 ,<br />

Pedro Lourenço 1 & Theunis Piersma 1,2<br />

1 Animal Ecology <strong>Group</strong>, Centre for Ecological and<br />

Evolutionary Studies, University of Groningen,<br />

PO Box 14, 9750 AA Haren, the Netherlands<br />

2 Department of Marine Ecology, Royal Netherlands Institute<br />

for Sea Research (NIOZ), PO Box 59, 1790 AB Den Burg,<br />

Texel, the Netherlands<br />

Although the Netherlands is a stronghold of the breeding<br />

population of the Black-tailed Godwit Limosa limosa limosa,<br />

numbers have declined severely over recent decades. Low<br />

reproductive success due to intensified agricultural management<br />

is the main reason. We compared the hatching success<br />

of godwit nests on extensively managed agricultural land with<br />

that of nests in intensively managed land, and between nests<br />

with various amounts of nest protection. This study shows<br />

that hatching success in intensively managed areas is very low<br />

(~24 %); almost half that recorded in the extensively managed<br />

areas (50 %). Hatching success on ‘grass islands’, areas of<br />

unmown grass left by farmers around occupied nests when<br />

the meadow is mown, is relatively low: 34% on large grass<br />

islands and 13% on small grass islands. This is of concern,<br />

because mowing intensively managed land invariably takes<br />

place before godwit nests hatch.<br />

Dramatic declines in shorebirds in<br />

Suriname and French Guiana<br />

R.I. Guy Morrison 1 , R.K. Ross 1 , Otte Ottema,<br />

Nyls de Pracontal, Thomas Pagnon & David Mizrahi<br />

1<br />

Environment Canada, National Wildlife Research Centre,<br />

Carleton University, 1125 Colonel By Drive (Raven Road),<br />

Ottawa, Ontario, Canada, K1A 0H3<br />

Guy.Morrison@ec.gc.ca<br />

The Canadian Wildlife Service “Atlas” studies of shorebird<br />

distribution around South America in the 1980s indicated that<br />

the coasts of Suriname and French Guiana were of exceptional<br />

importance as a wintering area for shorebirds, supporting<br />

almost two million, mainly small sandpipers, during surveys<br />

in early Feb 1982. Aerial surveys were again carried out in<br />

early Dec 2008, using the same methods and same principal<br />

observers, to determine changes in shorebird numbers. The<br />

surveys revealed dramatic declines, with a total of 403,959 in<br />

Dec 2008, only 20.6% of the total of 1,957,163 in Feb 1982.<br />

Declines were seen across all size-classes of shorebirds and<br />

across a wide variety of species, and proportional declines<br />

were generally greater in Suriname than French Guiana.<br />

Although some habitat changes were observed, and no information<br />

is available on food resources or possible redistribution<br />

to other areas, the declines are thought likely to reflect<br />

the widespread declines in shorebird populations that have<br />

been observed in many parts of the world.<br />

National action plan for the declining breeding<br />

population of Ruff Philomachus pugnax in Estonia<br />

Hannes Pehlak 1 & Eve Mägi 2<br />

1<br />

Estonian University of Life Sciences<br />

Hannes.pehlak@eesti.ee<br />

2<br />

Estonian Environmental Board<br />

Ruff is one of the most numerous waders in the world, but<br />

its population breeding in wet grasslands in Europe has declined<br />

approximately ten times since the 1950s. The reasons<br />

for the decline surely include breeding habitat loss, probably<br />

accompanied by predation, climate change, and degradation<br />

of wintering grounds. The breeding population of Estonia has<br />

followed the regional collapse dropping from at least 2,000<br />

to just 10–30 breeding females over the last fifty years. The<br />

meadows of the Matsalu wetland complex have been the most<br />

important breeding area for Ruff in the country, supporting<br />

half the national population in the 1950s and the only regular<br />

breeding site known today. The first national action plan for<br />

the breeding population in Estonia was prepared in 2008. This<br />

prescribes management for 18 potential Ruff breeding sites<br />

(28 km 2 ) comprising coastal and alluvial grasslands in W<br />

Estonia. The habitat needs of other endangered species were<br />

considered when drawing up management guidelines. Estonian<br />

coastal meadows are valuable e.g. as breeding sites for<br />

Southern Dunlin Calidris alpina schinzii and Natterjack Toad<br />

Bufo calamita, and as stopover sites for Lesser White-fronted<br />

Goose Anser erythropus. In managing grassland habitats for<br />

Ruff, mowing, combined with grazing where possible, should<br />

be preferred to grazing alone. In the sites where the existing<br />

management was suitable for achieving conservation targets,<br />

no change was suggested. Current plans include monitoring<br />

recently-used breeding sites, inventories of potential breeding<br />

sites, and research on the reasons for the decline. The action<br />

plan stresses the importance of continuous international cooperation<br />

for the success of Ruff conservation.<br />

When will we encounter the first silent spring<br />

Predicting the fall of the Dutch Black-tailed Godwits<br />

Julia Schroeder 1,2 , Jos Hooijmeijer 1 ,<br />

Martin Hinsch 3 & Theunis Piersma 1<br />

1<br />

Animal Ecology <strong>Group</strong>, Centre for Ecological and Evolutionary<br />

Studies, University of Groningen, the Netherlands<br />

2<br />

Current address: Animal and Plant Sciences, University of<br />

Sheffield, UK; julia.schroeder@gmail.com<br />

3<br />

Theoretical Biology <strong>Group</strong>,<br />

Centre for Ecological and Evolutionary Studies,<br />

University of Groningen, the Netherlands<br />

To improve the bleak situation of breeding Black-tailed godwits<br />

in the Netherlands, we can either aim to improve survival<br />

or productivity. A more detailed knowledge of how much<br />

we have to improve either one can equip us with knowledge<br />

on where to place the levers that might enable us to stop the


230 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

population decline. We make use of empirically gathered<br />

demographic estimates to predict the future of Black-tailed<br />

godwits in the Netherlands with the help of an analytical<br />

population model. Under the best conditions (high adult<br />

survival and high reproductive output) the Dutch breeding<br />

population of Black-tailed godwits will drop under 15,000<br />

breeding pairs as early as 2060, while when we assume<br />

more realistic starting values, we predict fewer than 10,000<br />

breeding pairs by 2030. Survival is hard to modify, given the<br />

already very high annual survival of godwits. Therefore we<br />

aim at predicting how much reproduction has to improve to<br />

stabilize the population decline. Under the very best scenario,<br />

which is rather optimistic, reproductive success must reach<br />

values of at the very least 0.85 fledged young per pair and year<br />

for every godwit pair breeding in the Netherlands for every<br />

year. The realization of this will be difficult, as it has to be<br />

negotiated with respect to economical expectations of grassland<br />

owners. We conclude that the goal to stop the population<br />

decline of Black-tailed godwits breeding in the Netherlands<br />

is a very ambitious and heartening goal, but not a realistic<br />

one under the current conditions. In the light of the demands<br />

of agricultural politics and economics, it is questionable if<br />

we will be able to take the measures necessary to stop or at<br />

the very least slow the decline of the Black-tailed godwit in<br />

the Netherlands.<br />

Assessing the health status of Wadden Sea birds<br />

Philipp Schwemmer 1 , Nils Guse 1 , Ursula Siebert 1 ,<br />

Stefan Garthe 1 , Ellen Prenger-Berninghoff 2 ,<br />

Reinhard Weiss 2 & Peter Wohlsein 3<br />

1<br />

Research and Technology Centre, University of Kiel,<br />

Hafentörn 1, 25761 Büsum, Germany<br />

schwemmer@ftz-west.uni-kiel.de<br />

2<br />

University of Gießen, Frankfurter Straße 94,<br />

35392 Gießen, Germany<br />

3<br />

University of Vetinerary Medicine Hannover,<br />

Bünteweg 17, 30559 Hannover, Germany<br />

For several years, various shorebird species have shown<br />

strong population declines in the Wadden Sea. The reasons<br />

for these declines are still poorly understood. We set up a<br />

pilot study to investigate possible relationships between the<br />

declines and the health status of Wadden Sea birds. Dead<br />

birds were collected along the German North Sea coast by<br />

a network of members of the National Park Service and different<br />

NGOs. Besides recording body condition, a detailed<br />

autopsy was performed. All organs were investigated macroscopically<br />

and nutritional status was assessed based on fat<br />

reserves and condition of the pectoral muscle. Samples for<br />

further histological, microbiological, virological, serological,<br />

parasitological and toxicological investigations were taken.<br />

Overall body condition was poor in all species investigated<br />

(i.e. emaciation). The condition of birds found dead on the<br />

beach and those that had been killed by flying into a lighthouse<br />

did not differ, indicating a bad overall nutritional<br />

status. The condition index of immatures was significantly<br />

lower than that of adults, while there were no differences<br />

between the sexes. Preliminary results of the pathological<br />

investigations showed individuals with numerous lesions:<br />

Eurasian Oystercatchers Haematopus ostralegus and Eurasian<br />

Curlews Numenius arquata were among the species with most<br />

frequent pathological abnormalities. Histological findings<br />

revealed pneumonia, hepatitis and splenitis with bacterial<br />

and parasitic etiology most likely. We found peritonitis in all<br />

Shelducks Tadorna tadorna investigated as well as three cases<br />

of tuberculosis. A long-term assessment of the health status<br />

of Wadden Sea birds is strongly recommended in order to (1)<br />

discover diseases in bird populations at an early stage, (2)<br />

provide data that allow comparison of health status between<br />

years and (3) provide data that might eventually unravel the<br />

reasons for the population declines of Wadden Sea birds.<br />

White blood cells composition in the Common Snipe<br />

Gallinago gallinago during autumn migration<br />

R. Włodarczyk 1 , P. Minias 1 , K. Kaczmarek 2 ,<br />

T. Janiszewski 1 & A. Włodarczyk 3<br />

1<br />

Department of Teacher Training and Biodiversity<br />

Studies, University of Łódź, Banacha 1/3,<br />

90-237 Łódź, Poland; wradek@biol.uni.lodz.pl<br />

2<br />

Medical University, Kosciuszki 4, 90-419, Poland<br />

3<br />

Department of Clinical Physiology, Medical University,<br />

Mazowiecka 6/8, 92-215, Łódź, Poland<br />

Common Snipes migrate in large numbers through inland<br />

water bodies in central Europe. They move slowly toward<br />

their wintering grounds in small steps. As a result, to some<br />

extent there is a temporal overlap between autumn migration<br />

and body- and wing-feather moult. This creates an<br />

opportunity to study the impact of both processes on the<br />

birds’ physiological state. In autumn 2008, >350 Common<br />

Snipes were caught at Jeziorsko reservoir, central Poland.<br />

Each bird was aged, measured, weighed and its moult stage<br />

was noted. For 87 individuals (64 juveniles and 23 adults)<br />

blood samples were taken in order to prepare blood smears.<br />

The smears were used for examination of white blood cell<br />

composition. The smears were stained by the May Grunwald<br />

and Giemsa technique. A proportion of each white cell fraction<br />

was analyzed using standard counts of 100 cells under a<br />

microscope at a magnification of 100× with oil immersion.<br />

The cells were identified using avian haematology guides.<br />

The heterophil:lymphocyte ratio was used as an indicator<br />

of physiological state. The most common were two types<br />

of cells: heterophils and lymphocytes. Three other groups<br />

(eosinophils, basophils and monocytes) did not exceed 20 %<br />

of all white cells. The heterophil/lymphocyte ratio varied significantly<br />

between individuals (range 0.12–11.2). There was<br />

no difference in H:L ratio between adult and juvenile snipes.<br />

This factor was negatively correlated with the weight of the<br />

bird (r = –0.30, df = 1, p = 0.005). Heavy individuals tended<br />

to have a low H:L. Other indicators of body condition such<br />

as wing-length and fat score were not correlated with white<br />

blood cell composition. Similarly sampling date and moult<br />

stage were not correlated with the H:L ratio.<br />

The status of Slender-billed Curlew and<br />

survey of potential sites in Iran<br />

Sadegh Sadeghi Zadegan<br />

National Manager, UNEP/GEF Siberian Crane Wetlands<br />

Project, Hemmat Highway, Pardisan Eco-Park,<br />

Dept. of Environment, PO Box 14155-7383 Tehran, Iran<br />

sadegh64@hotmail.com<br />

Observations along the Persian Gulf and Oman Sea indicate<br />

that in the vast coastal wetlands of Iran a few Slender-billed<br />

Curlews may still winter. There is virtually no wader hunting


Annual Conference<br />

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in Iran, at least for food (because the meat is not considered<br />

Halal) and therefore, usually hunters are not interested in<br />

shooting waders. Also, current hunting laws prevent any<br />

illegal shooting of waders and the Slender-billed Curlew is<br />

classified as an endangered bird.<br />

Waterbird counts have been conducted in most areas for<br />

several years. During 1963–1998 there are 42 records of<br />

Slender-billed Curlew (including 19 confirmed and 23 unconfirmed<br />

records). Two expeditions in early 2000 and one in<br />

2002 failed to locate birds although large areas of apparently<br />

suitable habitats still exist. A massive and specific survey for<br />

Slender-billed Curlew is being planned by the Department of<br />

Environment for winter 2010.<br />

Counts of the intertidal zones should ideally be executed<br />

at high tide, when birds are often concentrated at high water<br />

roosts. During low tide, sample or spot counts could be made<br />

in order to determine foraging densities of waders, permitting<br />

extrapolation to larger areas. Special attention should<br />

be paid to concentrations of Eurasian Curlews Numenius<br />

arquata, Whimbrel N. phaeopus and Black-tailed Godwits<br />

Limosa limosa since Slender-billed Curlews might mix with<br />

these species. At several locations attempts will be made to<br />

determine flight movements at dawn of these species to find<br />

night roosts.<br />

Capacity building needs include: training for observers;<br />

developing a wader monitoring and estimation method for<br />

the Gulf coast of Iran; exchange of knowledge, especially<br />

on Slender-billed Curlews between professional international<br />

experts and Iranian ornithologists.<br />

Workshops<br />

Workshop: Connecting conservation & research:<br />

Combining the forces of science and conservation<br />

to turn round the fortunes of shorebirds<br />

JUTTA LEYRER 1,2 , PIET VAN DEN HOUT 1 & THEUNIS PIERSMA 1,2<br />

1<br />

Royal Netherlands Institute for Sea Research (NIOZ), PO Box 14, 1790 AB Den Burg, Texel<br />

2<br />

Animal Ecology <strong>Group</strong>, Centre for Ecological and Evolutionary Studies, University of Groningen,<br />

PO Box 14, 9750 AA Haren, the Netherlands<br />

At the start of the 21st century the majority of migratory wader (shorebird) populations are faced with serious<br />

threats. This commonly results from the continuous destruction of wetlands, their key habitat. Healthy wetlands<br />

are highly biodiverse and extremely vulnerable, and as functioning ecosystems particularly important for us<br />

humans for a sustained livelihood (artisanal fisheries, small-scale farming) and our well-being (effective water<br />

filtering and cleaning systems). In many parts of the world, wetlands have been seen as wastelands, or even as a<br />

source of threat (malaria). Many freshwater wetlands have been drained for agricultural use and mudflats have<br />

been reclaimed for settlement and urbanization. Wetlands are continuously squeezed by economic development<br />

and increasingly used for recreational activities, and their resources are, in general, notoriously overexploited.<br />

Clearly, wetlands are in dire need of better protection. That is why numerous non-governmental organizations<br />

have taken on the task of convincing politicians and decision makers about the importance of safeguarding<br />

nature in general and wetlands in particular. To protect wetland habitats successfully, we need some level of<br />

understanding of the functioning of these ecosystems and the needs (or even the status) of the (wader) species<br />

occurring there, especially if they connect wetlands in different parts of the world by their migrations.<br />

Migrant waders seasonally use sequences of habitats on a global scale. This yields complications for both<br />

research and conservation. The performance of waders in one habitat will be influenced by the conditions in<br />

another, even if that “other” habitat is found half a world away. In addition, the actual ecological functioning<br />

of a habitat may depend on these migrants. Thus, events leading to a population decline in one wetland can<br />

change the ecology of a connected, if remote, wetland (Fig. 1).<br />

That we are now in the process of establishing such global ecological links is due to ecological and biological<br />

research worldwide. In the science world, knowledge is distributed by publications in peer-reviewed journals. In<br />

this way research results are opened to public access and criticism; it provides a system for public feedback and<br />

correction. Yet, it is clear that scientific publications do not always find their way into the political conservation<br />

and public arenas as much as they should. Why is that so And what needs to be done to open up this way<br />

In this workshop, we focused on the conservation importance of basic research on the one hand, and problems<br />

with the use of this research by the globally active conservation organizations on the other. We wanted to bridge<br />

what often seems to be a communication gap between “active researchers” and “operational conservationists”.<br />

Both conservation and research necessarily need to be long-term, and in the face of a wetland biodiversity<br />

crisis and an increasing trend for short-term funding, a closer connection between these two branches is needed<br />

more than ever.


232 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

THE DAY’S PROGRAMME – PRESENTATIONS<br />

The day started off with a presentation by Han Olff, University<br />

of Groningen, the Netherlands, on Ecosystem science<br />

and conservation in the soft-bottom intertidal. Using the<br />

Wadden Sea as a case study, he demonstrated that a profound<br />

knowledge of key ecological processes and disruptions in<br />

these processes, have severe implications for conservation.<br />

The international Wadden Sea provides a key area for migrating,<br />

wintering and breeding shorebirds within the East<br />

Atlantic Flyway. It also forms a part of an intercontinental<br />

meta-ecosystem connected e.g. by migrating shorebirds<br />

with wintering areas in coastal Western Africa and breeding<br />

areas in the Arctic tundra (Fig. 1). Yet, the Wadden Sea, but<br />

also coastal West Africa, are connected with their respective<br />

neighbouring ecosystems by nutrient and material flows as<br />

well as commuting animals. Events in one of these areas<br />

will have knock-on effects to any of the other areas, making<br />

conservation a truly international responsibility but also an<br />

inter-ecosystem problem.<br />

Barend van Gemerden of BirdLife Netherlands introduced<br />

us to the mechanics of conservation with his talk on<br />

Dealing with Conservationists. He focused on the many levels<br />

of possible co-operations between conservation and research<br />

by highlighting the needs of the conservation world that could<br />

be addressed by researchers: comprehensive overviews on<br />

the status of flyways, species, sites, threats and opportunities,<br />

early warnings of e.g. population crashes, expertise in<br />

impact assessments, authoritative (and passionate) spokesmen,<br />

engaging supporters. In turn, conservation could provide<br />

(seeking) financial support for research projects, publicizing<br />

and popularizing of research topics, lobbying, and above all<br />

conservation action. He stressed the need not to work separately,<br />

but to join forces and connect.<br />

One example of a research project that collected evidence<br />

on fatal effects of nature destruction came from Danny<br />

Rogers and co-author Ken Gosbell, Australasian <strong>Wader</strong><br />

Studies <strong>Group</strong>, Australia. The answer to the title of their talk<br />

Are tidal flat reclamations reducing shorebird numbers in<br />

the East Asian–Australasian Flyway is a clear firm “yes”.<br />

One of the most important shorebird sites in the Yellow Sea,<br />

Seamangeum, Republic of Korea, has been destroyed by reclamation<br />

of an area whose future use is still uncertain. A joint<br />

initiative by Birds Korea and the Australasian <strong>Wader</strong> Studies<br />

<strong>Group</strong> has documented the local and wider-scale effects<br />

of the Seamangeum reclamation on shorebirds. This work<br />

clearly showed that, despite the assurances and predictions<br />

by proponents of the reclamation project, displaced shorebirds<br />

did not simply move elsewhere but population sizes<br />

decreased dramatically after the closing of the Seamangeum<br />

seawall. Population decreases were exceptionally dramatic in<br />

Spoon-billed Sandpipers Eurynorhynchus pygmeus, and Great<br />

Knots Calidris tenuirostris. Counts of Great Knots in their<br />

NW Australian wintering areas have shown that the c.20% of<br />

Great Knots previously staging at Seamangeum have indeed<br />

gone “missing”. Although these birds have been lost, the<br />

evidence for the dramatic effects of Yellow Sea reclamations<br />

on shorebird populations should now empower conservation<br />

organizations to try harder and halt any further schemes.<br />

Red Knots Calidris canutus of the rufa subspecies have<br />

gained notoriety because of the dramatic population decline<br />

due to the tremendously deteriorating food resources (Horseshoe<br />

Crab eggs) in their main staging site during northward<br />

migration, Delaware Bay, USA. Yet, Delaware Bay is not<br />

the only site in trouble that is visited by these Red Knots<br />

within the annual cycle. Patricia M. González, Fundación<br />

Inalafquen and Global Flyway Network, Argentina, spoke<br />

about Conservation & Science – Red Knot Case in Patagonia<br />

Argentina. San Antonio Bay Natural Protected Area<br />

has been a Western Hemisphere Shorebird Reserve Network<br />

(WHSRN) <strong>International</strong> Site since 1993 and an Important<br />

Bird Area (IBA) since 2005, not least due to a combination<br />

of research projects studying demography, foraging ecology,<br />

migratory strategies, and habitat use of wintering Red<br />

Knots in the area and a series of successful projects on public<br />

awareness and education. It is a success story about what<br />

can be achieved when conservation and research go side by<br />

side, although the way to this point was long and arduous.<br />

Recent plans by the local government show that the work is<br />

far from over.<br />

Allan J. Baker, Royal Ontario Museum Toronto, Canada,<br />

gave an inspiring talk on how research and conservation bodies<br />

should take concerted action immediately. He pointed out<br />

that shorebird populations are plummeting worldwide and<br />

their habitats are highly endangered because of destructive<br />

exploitation by humans. He stressed that there is a much<br />

greater need for immediate conservation action than for early<br />

warning systems. Knowledge gained from research has to be<br />

the backbone of conservation action. This knowledge is sufficiently<br />

available to be implemented in conservation actions.<br />

Mike Pienkowski, UK Oversees Territories Conservation<br />

Forum, United Kingdom, and his co-authors David Stroud,<br />

Joint Nature Conservation Committee, United Kingdom, and<br />

Nick Davidson, Ramsar Convention Secretariat, Switzerland,<br />

gave tips and tricks on how we should go about Communicating<br />

conservation research to policy-makers. He pointed out<br />

that science and conservation operate in an immensely competitive<br />

information market where quality is but one criterion<br />

for survival. He therefore recommended that when “selling a<br />

story”, people should be aware of to whom they want to sell,<br />

and consequently should select the appropriate format (“one<br />

size doesn’t fit all”). There are some general rules though, and<br />

these are: present “the big picture”, keep it short and simple,<br />

and repeat your message again and again. He emphasized the<br />

importance of gaining an understanding about who one wants<br />

to influence and how they work. He emphasized that decision<br />

makers hardly ever come to researchers or conservationists;<br />

almost invariably it will be the other way round. Thus, lobbying<br />

is important, as well as to keep repeating the message<br />

again and again.<br />

THE DAY’S PROGRAMME – DISCUSSIONS<br />

Discussions in groups formed a central part of the workshop.<br />

We focused on the question whether there is indeed<br />

a communication gap between research and conservation.<br />

Each group presented their results and all confirmed the existence<br />

of such a communication gap. Although researchers<br />

and conservationists may share the passion to protect what<br />

they see and study, the “culture” of discussion and communication<br />

is different. While conservationists strive to find a<br />

“common base”of knowledge and perception, scientists are<br />

used to critical, challenging and often controversial discussions.<br />

Competition for money was named as another reason<br />

for a communication gap, especially between applied and<br />

basic research. Since conservation is in need of “fast” and<br />

“applicable” results, applied research has, very often, an<br />

advantage in the fight for monetary support. Yet, every group


Annual Conference<br />

233<br />

emphasized the importance of deep long-term studies that try<br />

and achieve an understanding of key ecological processes to<br />

develop sound nature conservation strategies.<br />

Interestingly, it was pointed out that in countries where<br />

well developed research and conservation is missing, there<br />

is no communication gap, as the same few people must take<br />

care of everything. Thus, ironically, where there are communication<br />

gaps, the worlds of both science and conservation<br />

are rather well developed!<br />

WHAT NEEDS TO BE DONE TO CLOSE THE GAP<br />

If we want to close the communication gap – and who doesn’t<br />

– we need to build bridges. And bridges are always best built<br />

from both sides of the divide. The prime responsibility of<br />

scientists is to do excellent science. Yet, they need to make<br />

an effort to communicate their findings to outsiders, including<br />

the relative outsiders and otherwise specialized workers in<br />

conservation organizations. They should try harder to publish<br />

in journals like Bird Conservation <strong>International</strong>, the science<br />

journal of BirdLife <strong>International</strong>, and the Journal of Applied<br />

Ecology, the applied journal of the British Ecological Society.<br />

Scientists may also become more involved in activities such<br />

as “horizon scanning” (see W.J. Sutherland et al. (2009) in<br />

Trends in Ecology and Evolution 24: 523–527), which in our<br />

specific case would mean the search for ecological factors that<br />

may have implications for shorebird populations and their<br />

habitats; to look out for “early warnings”.<br />

At the same time the conservation organizations should<br />

take a much greater responsibility in guiding communicating<br />

scientists, and perhaps even more importantly, realize (and act<br />

upon this realization) that they represent the most important<br />

societal voice for high quality ecological science. They can<br />

plead before national governments and international agencies<br />

to support excellence in ecological research, rather than take<br />

such science for granted. Conservation organizations can<br />

make excellent advocates for good ecology thus supporting<br />

ecologists to develop and realize the best possible ecological<br />

science including the maintenance of long-term research and<br />

monitoring efforts.<br />

By bridging the gaps we can achieve positive feedback:<br />

science will critically inform conservation, and conservation<br />

will critically help science to achieve the best possible<br />

understanding. We need to make research activities more<br />

relevant to the needs of conservation and unite in stopping<br />

those hell-bent on regardless exploitation.<br />

Temperate intertidal flats:<br />

part of a global meta-ecosystem<br />

Temperature rise<br />

Arctic tundra<br />

Acidification<br />

Temperature rise<br />

Northern<br />

Atlantic<br />

Acidification<br />

Temperature rise<br />

North Sea<br />

Sea level rise<br />

Temperature rise<br />

Wadden Sea<br />

gullies<br />

foredelta<br />

sublittoral<br />

banks<br />

Intertidal<br />

flats<br />

NW European<br />

lowlands<br />

Fisheries<br />

Fisheries<br />

Eutrophication<br />

Tropical Atlantic<br />

coastal zone<br />

Fisheries<br />

W African<br />

inter-tidal<br />

areas<br />

e.g. Banc d’Arguin<br />

Sahara,<br />

Sahel<br />

Overgrazing<br />

Desertification<br />

Exchange of sediments, detritus, nutrients, energy through tidal currents<br />

Daily and seasonal migration of birds, fish, mammals, invertebrates<br />

Fig. 1. The Wadden Sea, a key area for shorebirds within the East Atlantic Flyway, forms part of an intercontinental meta-ecosystem. It is connected<br />

to the Arctic breeding grounds and the West African wintering areas by migrating birds. Additionally, each of the habitats is connected<br />

to neighbouring ecosystems by both commuting animals and nutrient flows. Yet, the Wadden Sea, and also its connected ecosystems are<br />

threatened by exploitation and intensive usage by humans, as well as climate change (graphic courtesy of Han Olff, University of Groningen).


234 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (1) 2009<br />

Workshop: Monitoring waders in the Siberian Arctic<br />

BRUNO ENS 1 & HANS VERDAAT 2<br />

1<br />

SOVON Dutch Centre for Field Ornithology. bruno.ens@sovon.nl<br />

2<br />

Wageningen IMARES. hans.verdaat@wur.nl<br />

Large numbers of waders migrating along the East Atlantic and other flyways depend on the Siberian Arctic<br />

as a breeding area. In recent years, the monitoring effort of waders in the Siberian Arctic has declined. Yet,<br />

monitoring effort should have increased, because it is almost certain that global climate change will increasingly<br />

impact these waders in the years to come. This observation was the starting point for this workshop. We<br />

hoped to cover the following topics and questions:<br />

• The causes for the declining monitoring effort.<br />

• What have we learnt from monitoring efforts in the Siberian Arctic to date<br />

• How is monitoring organized in other parts of the arctic and what can we learn from those efforts<br />

• Which phenomena can probably only be explained by arctic breeding conditions<br />

• For which types of measurements do we really need to visit the Siberian Arctic<br />

• What are the most important topics that monitoring should address<br />

• What is the most efficient way to organize arctic monitoring Visit many different places in one season, or<br />

stay an entire season in one place<br />

• What can we do to reverse the declining effort<br />

ABSTRACTS OF WORKSHOP TALKS<br />

Monitoring of waders in the Siberian Arctic<br />

Mikhail Soloviev<br />

Dept. of Vertebrate Zoology, Moscow State University,<br />

Moscow, 119991, Russia; mikhail-soloviev@yandex.ru<br />

According to the official position, nature monitoring in the<br />

Russian Arctic should primarily be based on studies conducted<br />

in nature reserves, occupying considerable areas in<br />

different parts of Siberia. In practice, arctic nature reserves<br />

do not have sufficient human resources for intensive ornithological<br />

monitoring so this has been conducted during the<br />

last 20 years in a variety of expeditions. Information from<br />

these expeditions is accumulated in the on-line database of<br />

the Arctic Birds Breeding Conditions Survey (http://www.<br />

arcticbirds.net/); however, the total number of sites visited<br />

dropped from 39–60 in 2000–2007 to 35 in 2008.<br />

The number of sites where intensive wader monitoring has<br />

been conducted has never exceeded five in the whole Russian<br />

Arctic, but according to preliminary information this was<br />

reduced to only two programs in 2009: the <strong>Wader</strong> monitoring<br />

project on Taimyr (WMP) and the Monitoring of the Spoonbilled<br />

Sandpiper project on southern Chukotka. This decline<br />

is primarily explained by financial and logistical difficulties,<br />

including very high costs of local transportation. WMP has<br />

proved to be the most durable wader monitoring program in<br />

the Russian Arctic, and was carried out during 1994–2003<br />

and 2008–2009 in the south-eastern part of Taimyr and in<br />

2004–2007 in central Taimyr. The particular features of WMP<br />

are: consistency of principal monitoring protocols and core<br />

research teams over the whole period, double-sampling, surveys<br />

on plots in different habitats. The considerable duration<br />

of WMP allows us to discuss trends in numbers of breeding<br />

waders and to show statistically that nesting success of waders<br />

depends on numbers and activity of predators, and not on<br />

the abundance of alternative prey (lemmings). Evaluation of<br />

fledging success in arctic-breeding waders remains a difficult<br />

challenge that needs to be addressed in future monitoring<br />

activities.<br />

Results of monitoring waders in Medusa Bay<br />

Bas van den Boogaard 1 & Bruno Ens<br />

Working <strong>Group</strong> on <strong>International</strong> Waterbird and Wetland<br />

Research, the Netherlands; bvandenboogaard@gmail.com<br />

Between 1997 and 2007, a standardized monitoring program<br />

was carried out at Medusa Bay, Taimyr, Russia. The program<br />

had a focus on the number of breeding waders and related<br />

biotic and abiotic variables affecting breeding success. A key<br />

feature of this program is that it was carried out by volunteers<br />

from the Working <strong>Group</strong> on <strong>International</strong> Waterbird and Wetland<br />

Research (WIWO), combined with input from Russian<br />

researchers. To illustrate the value of this program, we present<br />

data of the number of breeding waders in fixed sample plots,<br />

and the corresponding lemming cycle, snowcover/weather<br />

phenology and breeding predators between 1997 and 2007.<br />

Besides six wader species and two species of bird of prey, we<br />

also present data on four songbird species.<br />

The advantage of WIWO expeditions is that costs are relatively<br />

low. However, because volunteers collect the data, they<br />

often become scattered among people, and this makes data<br />

analysis problematic, not least because volunteers suffer from<br />

a chronic shortage of time once the expedition has ended. We<br />

will discuss issues related to data analysis within programs<br />

based on volunteers, and future prospects for research at<br />

Medusa Bay or elsewhere on Taimyr.<br />

234


Annual Conference<br />

235<br />

<strong>Wader</strong> monitoring in high-arctic NE Greenland –<br />

low densities in a vast landscape<br />

Hans Meltofte 1 & Jannik Hansen<br />

1<br />

National Environmental Research Institute, University of<br />

Aarhus, PO Box 358, DK-4000 Reokilde, Denmark<br />

mel@dmu.dk<br />

Location of nests e.g. by rope-dragging is often considered<br />

the most reliable method for arctic wader censusing, but on<br />

thinly-populated high-arctic tundra, where surveys need to<br />

cover extensive areas, this is not realistic. Furthermore, even<br />

intensive nest search may miss up to 40% of the pairs due<br />

to predation, missed nests etc. Therefore, territory mapping<br />

must be considered as a time-efficient alternative. To obtain<br />

reliable population figures, territory mapping should ideally<br />

take place in the short interval between dispersal of the last<br />

birds on territories and initiation of incubation when birds<br />

become hard to record. In practice, the timing needs to be a<br />

compromise, which in the high Arctic is best obtained in mid<br />

June, when the birds are most active with song and other territorial<br />

behaviour. Population censusing in July only records<br />

successful pairs and hence, produce highly underestimated<br />

densities. In this presentation, the methods of 14 years of<br />

wader censuses at Zackenberg Research Station in central<br />

NE Greenland are discussed and compared to results from<br />

rope dragging and nest search.<br />

Fluctuations in breeding populations of waders at<br />

Zackenberg, NE Greenland, 1996–2009<br />

Jannik Hansen 1 & Hans Meltofte<br />

1<br />

Korsgade 11, st. Mf., 2200 Copenhagen N, Denmark<br />

jannikh@jannikh.dk<br />

We present data on breeding populations collected according<br />

to the early territory mapping method developed for the<br />

BioBasis monitoring programme at Zackenberg Research<br />

Station in central NE Greenland. Results are presented on the<br />

importance of early season snow cover, food availability and<br />

predation. NE Greenland is generally quite favourable to waders<br />

with sunny weather in most years, and only few inclement<br />

weather events occurred during the study years. Timing of<br />

egg-laying and most likely even population densities are<br />

determined by early season food availability, overruled in<br />

snow-rich years by extensive early season snow cover. Also<br />

food availability for chicks in July seems to influence recruitment<br />

in some species. Predation levels do not follow the<br />

lemming population fluctuations to the extent seen in other<br />

parts of the Arctic. Consequences of possible future climate<br />

changes are discussed.<br />

What do we need to monitor in the Siberian arctic<br />

in the face of global climate change<br />

Hans Schekkerman<br />

SOVON Dutch Centre for Field Ornithology,<br />

Rijksstraatweg 178, 6573 DG Beek-Ubbergen,<br />

the Netherlands; hans.schekkerman@sovon.nl<br />

Global climate change is affecting ecosystems worldwide, but<br />

the pace, magnitude and impact of changes to be expected are<br />

relatively large in the Arctic. As most arctic breeding birds are<br />

migratory, changes there may affect bird populations throughout<br />

the world. In this talk I will outline the most important<br />

environmental factors influencing shorebirds during their<br />

sojourn in the Arctic and from this derive a set of parameters<br />

that can be monitored to enable us to interpret changes in<br />

population size and demography that can be observed in other<br />

parts of these species’ migratory ranges.<br />

Remote sensing of conditions in the Arctic<br />

Valentijn Venus 1 , Andrew Skidmore et al.<br />

1<br />

<strong>International</strong> Institute for Geo-Information Science and<br />

Earth Observation (ITC), PO Box 6, 7500 AA Enschede,<br />

The Netherlands<br />

Remote sensing offers the hope of accurately monitoring<br />

conditions in inaccessible areas at a high spatial and temporal<br />

resolution covering vast areas. In theory historical conditions<br />

may be inferred from stored satellite images. Ideally,<br />

we would like to have information on snow coverage and<br />

how it changes in the course of the season, changes in the<br />

area of perma frost, weather conditions, vegetation types and<br />

phenology of the vegetation. As is often the case, theory is<br />

much better than practice. It turns out that remote sensing<br />

of conditions in the Arctic offers some special difficulties.<br />

For instance, since the sun is never high above the horizon,<br />

light hits the ground at a low angle. The talk will discuss the<br />

possibilities and limitations of remote sensing the conditions<br />

in the arctic.<br />

The Arctic Species Trend Index and wader trends<br />

Christoph Zöckler 1 on behalf of the Circumpolar<br />

Biodiversity Monitoring Programme<br />

UNEP-WCMC 219 Huntingdon Road Cambridge CB3 0DL,<br />

UK; christoph.zockler@unep-wcmc.org<br />

For the first time, an index providing a circumpolar perspective<br />

on trends in the Arctic’s living resources has been<br />

developed. The Arctic Species Trend Index (ASTI), like the<br />

global Living Planet Index (LPI), illustrates overall vertebrate<br />

population trends by integrating vertebrate population trend<br />

data from across the Arctic and over the last 40 years (1970<br />

as the baseline). This index not only allows for a composite<br />

measure of the overall trajectory of Arctic vertebrate populations,<br />

but can be disaggregated, e.g. by species, biomes or<br />

Arctic layers, as highlighted in this report.<br />

A total of 965 populations of 306 species (representing<br />

35% of all Arctic vertebrate species) were used to generate the<br />

ASTI in 2009. In contrast to the global LPI (Loh et al. 2008),<br />

whose overall decline is largely driven by declines in tropical<br />

vertebrate populations, the ASTI indicates an overall increasing<br />

trend (+21%) in arctic vertebrate populations between<br />

1970 and 2005. However, very few wader populations have<br />

been included in the present ASTI. At present only seven<br />

sites across the Arctic provide trend data for waders from the<br />

breeding grounds. Long-term monitoring of Arctic migrants<br />

takes place across the globe at wintering and staging sites<br />

and although the migratory index contains 216 species and<br />

599 populations, many wader data from monitoring stations<br />

outside the Arctic have not yet been included.<br />

Many waders or shorebirds are in decline but the reasons<br />

are not fully understood and although changes in the Arctic<br />

such as snow-cover, humidity and increasing shrub-cover are<br />

recognized to have already impacted shorebirds, there are


236 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

many other factors outside the Arctic to consider in explaining<br />

the trends. Trend data of Arctic waders monitored on the<br />

non-breeding grounds are much more abundant, but difficult<br />

to integrate into the ASTI as they are measured outside the<br />

Arctic. From a few selected species the ASTI will be disaggregated<br />

by wader trends measured within and outside the<br />

Arctic illustrating the differences and gaps in the analyses.<br />

CHASM as part of the Arctic Council Circumpolar Biodiversity<br />

Monitoring Programme (CBMP) network already aimed<br />

to integrate circumpolar monitoring activities, but needs to be<br />

strengthened and re-activated to make full use of the many<br />

monitoring initiatives within the IWSG. Appropriate steps<br />

to develop methods that allow the full integration of trend<br />

information collected outside the Arctic into the ASTI will<br />

be discussed and a much stronger collaboration (CBMP) is<br />

proposed.<br />

Workshop: Recovering the Slender-billed Curlew<br />

NICOLA CROCKFORD, GRAEME BUCHANAN & ROB SHELDON<br />

Royal Society for the Protection of Birds, The Lodge, Sandy, Beds. SG19 2DL, UK<br />

Nicola.crockford@rspb.org.uk<br />

The Slender-billed Curlew Numenius tenuirostris is the rarest bird in the Western Palearctic, following major<br />

declines from the second half of the 19th century onwards, apparently due to over-hunting and habitat-loss.<br />

There has been no verified record of this critically endangered species for about a decade. A “last push” to<br />

find and save the species before it is too late was launched in Dec 2008 by the Slender-billed Curlew Working<br />

<strong>Group</strong> (see www.slenderbilledcurlew.net).<br />

The priority is a comprehensive survey of the non-breeding range (from Morocco to Japan), especially historical<br />

wintering and potential moulting sites, during 2009/2010, and beyond as necessary, with a view to satellite<br />

tagging to identify key sites, especially the breeding grounds. If research, e.g. using stable isotopes, can sufficiently<br />

narrow the search for the breeding grounds, then the survey may be extended to that area e.g. in 2010.<br />

The main objectives of the workshop were to discuss and improve several protocols drafted to guide the<br />

search and subsequent conservation action for the Slender-billed Curlew.<br />

Following an overview of the project from Nicola Crockford, Tom van der Have presented the protocol on<br />

search methods and Simon Delany spoke of plans to ensure maximum survey coverage including by encouraging<br />

international volunteers expert in bird identification and using the <strong>International</strong> Waterbird Census as the main<br />

framework for the search. Rob Sheldon highlighted lessons to be learned from the Sociable Lapwing project<br />

and Sadegh Sadeghi Zadegan outlined plans for surveying Slender-billed Curlews in Iran.<br />

Graeme Buchanan and Tom van der Have summarised research approaches being used to narrow the search<br />

for the bird, including use of stable isotopes to try to pinpoint the breeding grounds and using patterns of rainfall<br />

and orthoptera distribution to give clues to remaining suitable habitat. Bob Gill summarised lessons to be<br />

learned from the Eskimo curlew of North America.<br />

There followed discussions of various protocols on action to be taken once the species is relocated. Nigel<br />

Clark led the one on catching, handling and satellite tagging, with invaluable input from Bob Gill, Nils Warnock<br />

and Lee Tibbetts, Graeme Buchanan on ecological observations to make of the bird and Geoff Hilton on captive<br />

breeding. In addition Simon Delany led a discussion on using the Slender-billed Curlew search also to gather<br />

information on threatened steppe-breeding subspecies of Eurasian Curlew and Whimbrel.<br />

There seemed to be broad agreement among the participants as to the way forward. It is an abnegation of<br />

responsibility to do nothing, and if action is to be taken, it must be undertaken properly, with determination.<br />

Even if the search is unsuccessful in terms of finding the Slender-billed Curlew, it looks set to provide a number<br />

of other long term conservation benefits.<br />

ABSTRACTS OF WORKSHOP TALKS<br />

Searching for the Slender-billed Curlew:<br />

when, where and how<br />

Simon Delany 1 & Tom van der Have 2<br />

1<br />

Wetlands <strong>International</strong>; simon.delany@wetlands.org<br />

2<br />

Foundation WIWO<br />

The <strong>International</strong> Waterbird Census is an excellent framework<br />

for the extra effort needed to find the Slender-billed Curlew. A<br />

protocol is proposed listing which actions should be taken to<br />

maximise the chance of observing the species, including during<br />

the planned waterbirds counts and wetlands surveys in the<br />

range states. Emphasis is on good preparations, accurate identification,<br />

awareness of confusing species and rapid response<br />

if a Slender-billed Curlew is found. Teamwork is needed if<br />

a bird is located to keep track of its whereabouts to facilitate<br />

possible catching efforts and conservation measures. Several<br />

suggestions are given about timing (winter period preferred),


Annual Conference<br />

237<br />

location (for example, former range states), habitat (look for<br />

wetland roosts and dryer foraging habitats like grasslands,<br />

steppe and saltmarsh) and field skills (make mental image of<br />

preferred habitat and SBC jizz and calls, become familiar with<br />

confusing species, check roosts and so on). The Slender-billed<br />

quest is seriously hampered by the fact our current knowledge<br />

of foraging habitat is based on only the three adult males that<br />

wintered in Merja Zerga, Morocco. We do not really know its<br />

preferred food and foraging habitat, and there is still a chance<br />

that the remaining individuals are overlooked in areas not<br />

visited by birdwatchers.<br />

Plans for maximizing survey coverage and<br />

participation by observers<br />

Simon Delany<br />

Wetlands <strong>International</strong>; simon.delany@wetlands.org<br />

The <strong>International</strong> Waterbird Census coordinated by Wetlands<br />

<strong>International</strong> provides a good framework for the forthcoming<br />

search for Slender-billed Curlews. The Census includes most<br />

of the sites where the species has been recorded, and over<br />

10,000 observers, mostly volunteers, will be in the field in<br />

January 2010 counting waterbirds within the former wintering<br />

range of the species. Waterbird counters are often not,<br />

however, well-placed to find and identify rarities because<br />

the need to separate and count the numerous species at a site<br />

is usually a full-time job. An approach already adopted in<br />

Italy is proposed, where observers accompany counters in<br />

the field and concentrate on finding less numerous species,<br />

especially unusual curlews. This approach has already been<br />

promoted in a July 2009 Newsletter to national coordinators<br />

of waterbird monitoring schemes, and to a large number of<br />

visitors to the UK Birdfair. There is now a need to recruit<br />

more birders, to accompany counters in the field, through web<br />

fora and discussion groups. We will also extend the approach<br />

to sub-Saharan Africa and Asia, but the top priority remains<br />

the known former range of Slender-billed Curlew.<br />

The status of Slender-billed Curlew and survey of<br />

potential sites in Iran<br />

Sadegh Sadeghi Zadegan<br />

National Manager of UNEP/GEF SCWP,<br />

Department of Environment, Iran<br />

Observations along the Persian Gulf and Oman Sea indicate<br />

that in the vast coastal wetlands of Iran a few Slender-billed<br />

Curlews may still winter. There is virtually no wader hunting<br />

in Iran, at least for food (because the meat is not considered<br />

Halal) and therefore, usually hunters are not interested in<br />

shooting waders. Also, current hunting laws prevent any<br />

illegal shooting of waders and the Slender-billed Curlew is<br />

classified as an endangered bird.<br />

Waterbird counts have been conducted in most areas for<br />

several years. During 1963–1998 there are 42 records of<br />

Slender-billed Curlew (including 19 confirmed and 23 unconfirmed<br />

records). Two expeditions in early 2000 and one in<br />

2002 failed to locate birds although large areas of apparently<br />

suitable habitats still exist. A massive and specific survey for<br />

the species is being planned by the Department of Environment<br />

for winter 2010.<br />

Counts of the intertidal zones should ideally be executed<br />

at high tide, when birds are often concentrated at high water<br />

roosts. During low tide, sample or spot counts could be made<br />

in order to determine foraging densities of waders, permitting<br />

extrapolation to larger areas. Special attention should<br />

be paid to concentrations of Eurasian Curlews Numenius<br />

arquata, Whimbrel N. phaeopus and Black-tailed Godwits<br />

Limosa limosa since Slender-billed Curlews might mix with<br />

these species. At several locations attempts will be made to<br />

determine flight movements at dawn of these species to find<br />

night roosts.<br />

Capacity building needs include: training for observers;<br />

developing a wader monitoring and estimation method for<br />

the Gulf coast of Iran; exchange of knowledge, especially<br />

on Slender-billed Curlews between professional international<br />

experts and Iranian ornithologists.<br />

Stable isotopes<br />

Graeme Buchanan<br />

Royal Society for the Protection of Birds, The Lodge,<br />

Sandy, Beds. SG19 2DL, UK<br />

graeme.buchanan@rspb.org.uk<br />

The ratios of different isotopes of elements (e.g. 13 C and<br />

12 C) display geographic variation. Combinations of multiple<br />

elements can be used to identify where samples with specific<br />

ratios may have come from. This applies to bird feathers,<br />

since the isotopes pass up the food chain, and are assimilated<br />

into body tissues. We are fortunate in having some 100<br />

feather samples from Slender-billed Curlew specimens, for<br />

which we are grateful to various museums and collections.<br />

Analysis of these samples is being used to determine potential<br />

breeding areas, and potentially moult sites. Early results suggest<br />

Slender-billed Curlews could have bred in a band across<br />

southern Russia, and include the area where the few known<br />

breeding records come from. Additional analysis of further<br />

elements should refine the maps, enabling targeted searches<br />

of potential breeding areas.<br />

Slender-billed Curlew decline:<br />

loss of habitat, food and mates<br />

Tom van der Have<br />

Foundation WIWO; tom.vanderhave@wur.nl<br />

Knowing the factors that contributed to the near-extinction<br />

of the Slender-billed Curlew may help to narrow down the<br />

search to specific areas and habitats. The decline probably<br />

started in the last two decades of the 19th century. By the time<br />

the first and only nests were found in the second decade of the<br />

20th century it was already a rare bird. The steady decrease in<br />

numbers of specimens and observations continued until the<br />

last accepted record in 2001.<br />

A quantitative analysis of museum specimens showed that<br />

habitat loss and droughts in the breeding areas were probably<br />

the main cause of the decline. An increasing male-biased sex<br />

ratio exacerbated the difficulty of finding mates at dwindling<br />

densities. In addition, increasing hunting pressure in migration<br />

and wintering areas probably lowered survival rates far<br />

beyond sustainability.<br />

A long neglected aspect in its ecology is food choice.<br />

Orthoptera deserve further study as a potential resource<br />

during most of the year in breeding, stopover and wintering<br />

ranges. The extinction of the Rocky Mountain Grasshopper,<br />

an (if not the) important resource at the prairie spring staging


238 <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong> Bulletin 116 (3) 2009<br />

areas, most likely was one of the main factors leading to the<br />

demise of the Eskimo Curlew. The observation that orthoptera<br />

are an important element of the diet of curlews east of the<br />

Urals (G. Buchanan, pers. comm.) gets more significance in<br />

this context. Orthoptera are highly dependent on permanent,<br />

grazed or ungrazed grasslands which seem to fit the supposed,<br />

year-round habitat preference of Slender-billed Curlew. Several<br />

grasshopper species are discussed as serious suspects.<br />

Presentation of draft protocol on trapping,<br />

handling and satellite tracking<br />

Nicola Crockford 1 & Nigel Clark 2<br />

1<br />

Royal Society for the Protection of Birds, The Lodge,<br />

Sandy, Beds. SG19 2DL, UK<br />

Nicola.crockford@rspb.org.uk<br />

2<br />

British Trust for Ornithology. nigel.clark@bto.org<br />

It is proposed that a key objective of finding Slender-billed<br />

Curlews is to satellite track them to identify the sites they use<br />

and thus facilitate their conservation. In advance of finding<br />

Slender-billed Curlews, it is desirable to have a widely agreed<br />

protocol which outlines the justification and methods for<br />

catching, collecting information from and tagging this critically<br />

endangered species. Such a protocol will be outlined,<br />

including itemising the steps needed to prepare for rapid<br />

reaction in the event of a sighting of a probable slender-billed<br />

curlew, deployment of a catching/tagging team, and manage<br />

publicity. Discussions following the presentation of the protocol<br />

will be used to improve the draft document.<br />

Presentation of draft observation protocol<br />

Graeme Buchanan<br />

Royal Society for the Protection of Birds, The Lodge,<br />

Sandy, Beds. SG19 2DL, UK<br />

graeme.buchanan@rspb.org.uk<br />

The ecology of Slender-billed Curlew is very poorly known.<br />

Any information on the feeding ecology and diet will increase<br />

our knowledge, and potentially understanding of the needs<br />

of the species. To this end, a revised protocol has been produced,<br />

based on an earlier LIFE funded version, to ensure<br />

data are collected in an objective and comparable manner.<br />

It covers foraging habitats, energy budgets and diet. Discussions<br />

following the presentation of the protocol will be used<br />

to improve the draft document.<br />

Draft captive breeding protocol<br />

Geoff Hilton<br />

Wildfowl & Wetlands Trust, the Netherlands<br />

geoff.hilton@wwt.org.uk<br />

The premise of the ‘last push’ for conservation of the Slenderbilled<br />

Curlew is that, even though the rediscovery of the<br />

species might seem improbable, we should do all that we<br />

can to ensure that, if and when rediscovery does happen,<br />

we are adequately prepared to react decisively, rapidly and<br />

effectively to avert extinction. Allowing for the option of<br />

captive breeding is part of this preparation. Serious consideration<br />

should be given to the objectives, benefits and risks<br />

of establishing a captive population for arking, augmentation<br />

of the wild population, or reintroduction to new sites. It is<br />

important that clear thinking on this takes place in advance of<br />

the decision being made urgent by a rediscovery. In assessing<br />

whether establishing a captive population would be a useful<br />

conservation intervention, we need to know whether there<br />

is a high probability of success in captive breeding. We thus<br />

need to know how this would be achieved and what the implications<br />

would be for the remaining wild population. The<br />

prescription for a successful captive population would need<br />

to be tested and demonstrated so that practitioners have a<br />

“recipe” available to them at the point of need. To meet these<br />

needs, a trial programme with “proxy species”of wader would<br />

be sensible. We discuss how this might be achieved, the issues<br />

to be resolved, and the lessons that would be learned.<br />

Using the search for the Slender-billed Curlew<br />

to find rare and poorly known forms of<br />

Eurasian Curlew and Whimbrel<br />

Simon Delany<br />

Wetlands <strong>International</strong>; simon.delany@wetlands.org<br />

The search for the Slender-billed Curlew provides an opportunity<br />

to find individuals of other rare and poorly-known<br />

curlews. Numenius phaeopus alboaxillaris is extremely rare<br />

and probably winters mainly on coasts of the western Indian<br />

Ocean. Numenius arquata suschkini is known from only a<br />

few specimens and is usually ignored, but it is possibly or<br />

probably a valid and highly threatened sub-species. The rarity<br />

of these two small and pale forms, as well as the possibility<br />

of confusion with Slender-billed Curlew, make them very<br />

interesting subjects for study. Numenius arquata orientalis is<br />

relatively common, but less numerous than nominate arquata<br />

and also apparently declining. The Slender-billed Curlew<br />

search offers an opportunity to find out more about numbers<br />

and distribution of this sub-species.<br />

A recording form where observers can provide details of<br />

all curlews observed during surveys will be made available to<br />

download from the internet, and will be provided as electronic<br />

or hardcopy to anybody requesting it. The completed forms<br />

will provide valuable information on numbers and distribution<br />

of all sub-species of curlew in the winter of 2009–2010.<br />

The Slender-billed Curlew recovery effort: applicable<br />

insights from studies of New World Numeniini<br />

Robert Gill 1 , Nils Warnock 2 & Lee Tibbitts 1<br />

1 U.S. Geological Survey, Alaska Science Center,<br />

4210 University Drive, Anchorage, AK 99508, USA<br />

robert_gill@usgs.gov<br />

2 Wildlife Health Center, School of Veterinary Medicine,<br />

Univ. of California, Davis, CA 95616, USA<br />

The New World hosts 8 of 13 members of the tribe Numeniini<br />

(curlews and godwits). One, the Eskimo Curlew, went from<br />

being widespread and abundant to likely extinct in the span<br />

of a century.Populations of most of the other species are experiencing<br />

population declines. A better understanding of the<br />

causes of these declines is the underpinning of a major effort<br />

(Pacific Shorebird Migration Project, PSMP) launched in<br />

2005 that uses remote sensing technology, primarily satellite<br />

telemetry, to discern the movement ecology and conservation<br />

biology of Pacific Basin Numeniini.<br />

Through our studies we have gained some insights into<br />

the population dynamics of godwits and other curlew species


Annual Conference<br />

239<br />

that may be applicable to the current effort with the critically<br />

endangered Slender-billed Curlew. The story of the demise<br />

of the Eskimo Curlews offers a sobering reality check to the<br />

task at hand. In short, major human-caused perturbations over<br />

a 50-year period (suppression of fire, rapid and widespread<br />

fragmentation and conversion of habitats, extinction of a<br />

principal food source, and hunting of unprecedented scope)<br />

created a situation in which the Eskimo Curlew population<br />

fell below the minimum level of viability. This level appears<br />

to have been set by the species’ reliance on specialized and<br />

patchy habitat, its conservative life history, and its highly<br />

social behaviour – sadly all traits inherent to most Numeniini,<br />

including the Slender-billed Curlew. But, ignoring the<br />

disheartening similarities between the plights of Eskimo and<br />

Slender-billed Curlews and, given that much of society expects<br />

intervention with endangered wildlife, there are things<br />

learned from PSMP work and its use of satellite telemetry<br />

that may be applicable to the Slender-billed Curlew effort.<br />

From work with five species of Numeniini (n = 142<br />

transmitters to date, including 49 solar-powered units) and<br />

based on what we know about the biology of Slender-billed<br />

Curlews, we think satellite telemetry is a compatible tool to<br />

discern areas used and migratory routes taken during various<br />

phases of the species’ annual cycle. (Caveat lector – the following<br />

have worked for us, but this does not preclude use of<br />

other modifications.) Specifically, we recommend: 1) use of<br />

external-mounted, solar-powered models (e.g., Microwave<br />

12.5 g units), 2) attachment using a leg-loop harness (we<br />

strongly advise against wing or breast–abdomen harnesses on<br />

Numeniini), 3) modification of antennas to follow the dorsal<br />

contour of the bird and reduce costs of drag, 4) activation<br />

of a transmitter(s) as soon as possible within the suspected<br />

range of the curlew so that users can become familiar with<br />

the data system, 5) deployment of a transmitter on a similar<br />

migratory species within the suspected range of the curlew so<br />

that tracking can be tested in the region, and 6) establishment<br />

of a protocol prior to capture that details data collection and<br />

dissemination.<br />

Welcome to Lisbon!<br />

<strong>International</strong> <strong>Wader</strong> <strong>Study</strong> <strong>Group</strong><br />

Conference 2010<br />

The IWSG Annual Conference 2010 will be held in Lisbon, Portugal, hosted by the National Natural History<br />

Museum (NNHM) of Lisbon University. The NNHM has a very rich history both within its collections and<br />

also as an historical building lying at the heart of Lisbon, and also includes a magnificent Botanical Garden.<br />

The Conference Programme is still to be finalized, but the main sessions will take place on Saturday 2nd<br />

and Sunday 3rd October 2010. Unfortunately, the number of participants will be limited to approximately<br />

120 people so early registration is strongly recommended.<br />

However, we will be able to organize one or two thematic workshops. We therefore ask for all potential<br />

workshop organizers to send a short workshop proposal to the organizers to José Pedro Granadeiro<br />

(jpgranadeiro@fc.ul.pt) by 1st March 2010. Depending on the number of proposals, the organizing committee<br />

will select one or two workshops to be held at IWSGC 2010.<br />

Please check the IWSG website regularly to receive further information on registration and critical<br />

deadlines.

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