waders and their estuarine food supplies - Vlaams Instituut voor de ...
waders and their estuarine food supplies - Vlaams Instituut voor de ...
waders and their estuarine food supplies - Vlaams Instituut voor de ...
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PREDICTING SEASONAL AND ANNUAL FLUCTUATIONS IN THE LOCAL EXPLOITION OF DIFFERENT PREY<br />
nasi to the Wad<strong>de</strong>n Sea. mussel beds in the Exe do not<br />
disappear from gales <strong>and</strong> ice. such as occurs in ihc<br />
Wad<strong>de</strong>n Sea iDankers & koelemaij I"**). Obert &<br />
Michaelis 1991). Moreover, since ihe annual recruitment<br />
of Mussels in the Exe is less erratic than in the<br />
Wad<strong>de</strong>n Sea <strong>and</strong> the survival of spat siiongly negatively<br />
<strong>de</strong>nsity-<strong>de</strong>pen<strong>de</strong>nt, ihc <strong>de</strong>nsit) of large Mussels<br />
does not vary much (McGrorty et al. 1990).<br />
Were Oystercalchers <strong>de</strong>pen<strong>de</strong>nt on one or two prey<br />
species in the Wad<strong>de</strong>n Sea. they would not be able to<br />
survive a period longer than one to four years. The<br />
buds iii our study area could only stay alive by switching<br />
regularly from one lo another bivalve species <strong>and</strong><br />
lake, in total, four bivalve species during ihe ten years<br />
of observation (Fig. 14). Nevertheless, ihe intake rales<br />
would be insufficient during four years, <strong>and</strong> ihe birds<br />
had to move to alternative feeding areas. The high water<br />
counts showed thai the total number of Oystercatchers<br />
did nol <strong>de</strong>crease during these years along ihis<br />
part of the Frisian coast <strong>and</strong> the nearby isl<strong>and</strong> Engelsmanplaat<br />
(Zegers & Zwarts unpubl.). Therefore, the<br />
birds must have moved to feeding areas siill within<br />
reach of the same high water roosts. Sightings of<br />
colour-b<strong>and</strong>ed birds showed lhat many of the Nes<br />
birds moved to mussel beds on the lower shore, at 1 to<br />
4 km from the Nes area, ln other words, the birds could<br />
not survive a ten year period if they restricted <strong>their</strong><br />
feeding range to I km : of mudflats. However, by extending<br />
<strong>their</strong> individual feeding ranges in an area of<br />
10-20 km', they could probably find enough fcxxl.<br />
The large majority of Oystercalchers in the Wad<strong>de</strong>n<br />
Sea <strong>de</strong>pend in winter on Cockles <strong>and</strong> Mussels. The<br />
year-to-year variation in ihe ixcurrence of both prey is<br />
very large (Beukema ei al. 1993). Unfortunately for<br />
<strong>their</strong> predators, recruiimenl <strong>and</strong> mortality of both<br />
species is related to the winter temperature, by which<br />
ihe fluctuations of the <strong>food</strong> stock of both species lend<br />
to be synchronized (Beukema et al. 1993). Hence.<br />
()> stercatchers wintering in the Wad<strong>de</strong>n Sea must <strong>de</strong>al<br />
with a varying, <strong>and</strong> sometimes low. fcxxl supply.<br />
Are Oystercatchers limited by <strong>their</strong> <strong>food</strong> supply?<br />
Several prey species contribute to the benthic production,<br />
<strong>and</strong> since each bird species restricts its diet to a<br />
limited number of prey species <strong>and</strong> size classes, each<br />
bird species harvests only a part of ihe lotal production.<br />
Oystercalchers restrict <strong>their</strong> diet mainly to bi<br />
263<br />
valves. They consumed in the Nes area yearly 12<br />
g in'-'. on average, or 21*Jt of the total yearly elimination<br />
of the live bivalve species combined (Table I).<br />
The predation pressure by Oystercatchers on <strong>their</strong> pi e\<br />
has already often been measured, although usually not<br />
as traction of the annual prey elimination, but as frac<br />
tion of the total biomass being removed over the winter<br />
(see recent reviews by Meire 1993 <strong>and</strong> Goss-Custard<br />
el ul. 1996b). Oy stereatchers are able to remove<br />
between 10 <strong>and</strong> 80% of <strong>their</strong> prey m ., winter, but in<br />
most studies ti is 20 lo 40%. Also this study reveals a<br />
large variation in the predation pressure between prey<br />
species (Tables 1 & 2). <strong>and</strong> between years (Fig. 18). In<br />
S? 0.6 -<br />
i- °<br />
6<br />
E<br />
B 2.5<br />
c<br />
$<br />
2.0k<br />
1.5-<br />
1.0-<br />
10<br />
MILD<br />
20 30 40 50<br />
NORMAL COLD SEVERE<br />
Unsen frost in<strong>de</strong>x<br />
80. ®<br />
^\T2?<br />
- y=exp(l 02 - 0.616x)<br />
0.8-<br />
. r=0.91 p=0.03<br />
j j — i<br />
0.4 0.6 0.8<br />
i<br />
1.0<br />
•<br />
1.2<br />
i—<br />
1.4 1.6<br />
l . _ j _<br />
lowest intake rate (mg-s 1 1.8 2.0<br />
)<br />
Fin. 22. Winter mortality ol Ovstercalchers captured llonrj ihe<br />
i COOSl as a I'unclioii nl A. llie Unsen frost in<strong>de</strong>x <strong>and</strong> B. ihc<br />
predicted lowest intake rale in winter in the Nes area; a selection is<br />
ma<strong>de</strong> for recoveries in January-April. The analysis is based on 3424<br />
colour-b<strong>and</strong>ed Oystercatchers <strong>and</strong> exclu<strong>de</strong>d ihe yearlings: from<br />
/warts,/ ul. (IWbei. The frost in<strong>de</strong>x of Unsen 11991)19 <strong>de</strong>fined as<br />
0.000275V 3 + 0.667y + 1.11 Iz. where \ is the tuiiiibcr ol day l w Ufa<br />
a minimum temperature < 0 "C. <strong>and</strong> y <strong>and</strong> / the number of days with<br />
a maximum temperature < 0 C <strong>and</strong> < -II) '('. resp