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waders and their estuarine food supplies - Vlaams Instituut voor de ...

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Tabic 3. Average intake rale Img s ' ± SD) <strong>and</strong> prey weight per prev<br />

Species; n is the number of studies i given in appendix). Eleven stud­<br />

ies « uh a feeding period < 1 h <strong>and</strong> two studies with extremely low<br />

intake rates inrs. 190 & 197 in appendix) have been exclu<strong>de</strong>d.<br />

S/.i cii v mgr> SD mg PI<br />

Anadara 1.85 1637 1<br />

Arenicola 2.96 1.64 216 j<br />

Cerasto<strong>de</strong>rma 2.17 0.93 230 4S<br />

Eanhworms 1.18 0.5.' 71 5<br />

Littorina IM 0.27 138 8<br />

Macoma 2.34 0.59 67 12<br />

Mya 3.14 0.64 172 3<br />

Mytilus ventral 2.04 0.92 418 26<br />

Mytilus dorsal 2.10 0.93 513 27<br />

Mytilus si,,h 2.05 0.69 409 4S<br />

:.mi 0.95 61 23<br />

Patella 2.35 120 1<br />

Scrobicularia 1.74 (1.75 178 11<br />

Tipula 1.34 11.48 53 IS<br />

Uca 1.78 78 dl<br />

all species 2.00 0.85 24(1<br />

12 armoured prey species, <strong>and</strong> (4) intake rate differed<br />

between the species when prey of similar weight were<br />

taken.<br />

Table 3 gives the average intake rate per prey<br />

species. According to a one-way analysis of variance,<br />

the differences were significant (R 2 = 0.185, p < 0.0()I.<br />

n = 240). The highest intake rate was found in birds<br />

feeding on Mya or Arenicola <strong>and</strong> the lowest in birds<br />

eating earthworms. Tipula or Littorina. Since intake<br />

rate increased with prey weight in each prey species, a<br />

similar relationship might be expected between average<br />

intake rate <strong>and</strong> average weight across prey species.<br />

There was. however, no such relationship (r • 0.00).<br />

But in or<strong>de</strong>r to rule out any possible effect of prey si/e<br />

on intake rate, the intake rate was st<strong>and</strong>ardized to a<br />

prey weight of 200 mg. using the predicted values<br />

from the multiple regressions with a common slope but<br />

different intercepts for the different soft-bodied <strong>and</strong> armoured<br />

prey species. Intake rate averaged for each<br />

species now differed more from each other. In conclusion,<br />

prey weighl <strong>de</strong>termines to a large <strong>de</strong>gree the intake<br />

rate, but differences between the prey species are<br />

even larger.<br />

PREY PROFITABILITY AND INTAKE RATE<br />

194<br />

Intake rate <strong>and</strong> prey <strong>de</strong>nsity<br />

A review of the effect of prey <strong>de</strong>nsity on intake rate<br />

was only attempted for Oystercatchers feeding Cockles.<br />

We selected len cockle studies, from the 12 available.<br />

As discussed b\ Zwarts et al. (1996b) intake ratewas<br />

presumably overestimated by Goss-Custard<br />

(1977). while Triplet (1994a) does not present sufficient<br />

<strong>de</strong>tails to be inclu<strong>de</strong>d in the analysis.<br />

If birds do not vary <strong>their</strong> search rate <strong>and</strong> prey selection<br />

with prey <strong>de</strong>nsity, a type 2 functional response<br />

would be expected (Holling 1959). Although the levelling<br />

off in the intake rate al high prey <strong>de</strong>nsity in the experiments<br />

of Hulscher (1976) resembled this type of<br />

response (redrawn in Fig. 16). the assumptions un<strong>de</strong>rlying<br />

the mo<strong>de</strong>l were not met (Wanink & Zwarts<br />

1985). As had already been suggested by Hulscher<br />

(1976). the birds increasingly specialized on easy prey<br />

with short h<strong>and</strong>ling times when prey <strong>de</strong>nsity increased.<br />

Thus, even in a controlled experiment. Holling"s functional<br />

response equation was too simple to <strong>de</strong>scribe the<br />

reeding behav iour of Oystercatchers.<br />

The situation in the wild is still more complicated,<br />

because changes in prey <strong>de</strong>nsity are usually accompanied<br />

by variation in prev condition <strong>and</strong> prey size (e.g.<br />

Goss-Custard 1977, Sutherl<strong>and</strong> 1982a). Sutherl<strong>and</strong><br />

(1982a. b) compared the feeding behaviour of Oystercatchers<br />

visiting 12 plots where the cockle <strong>de</strong>nsity varied<br />

between 10 <strong>and</strong> 600 prey m " 2 . He found a levelling<br />

off in the feeding rate at about 9 Cockles min" 1 . However,<br />

the highest intake rate was achieved at low prey<br />

<strong>de</strong>nsities because prey were large where <strong>their</strong> <strong>de</strong>nsity<br />

was low: r = -0.90 for ln(<strong>de</strong>nsity) against prey weight.<br />

A multiple regression analysis revealed that the intake<br />

rate was highly <strong>de</strong>pen<strong>de</strong>nt on prey weight (R 2 = 0.417,<br />

p = 0.0(X)2) as well as on prey <strong>de</strong>nsity (R 2 = 0.407, p =<br />

0.001). With the exception of the plot with the lowest<br />

prey <strong>de</strong>nsity of 10 Cockles nr 2 , all these values of intake<br />

rate fitted rather well with the general relationship<br />

between intake rate <strong>and</strong> prey weight (Fig. 13).<br />

Intake rate as a function of prey weight <strong>and</strong> <strong>de</strong>nsity<br />

has also been calculated in a multiple regression of the<br />

combined data set for the 38 measurements taken from<br />

the ten studies on cockle-feeding birds <strong>de</strong>picted in Fig.<br />

16. Again, the effect of prey weight was highly significant<br />

(R 2 = 0.577, p < 0.001) as well as prey <strong>de</strong>nsity<br />

(R 2 = 0.093. p = 0.004), with a highly negative correlation<br />

between ln(<strong>de</strong>nsity) <strong>and</strong> In(prey weight) (r =

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