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

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VARIATION IN FOOD SUPPLY OF KNOT<br />

Macoma balihica<br />

Cerasto<strong>de</strong>niia edule<br />

1111111 1111111111111111111111111111111111111<br />

JJMMJSN'JMMjSN'JMMJSN'jMMJSN 1<br />

Fig. 5. Growth of five bivalve species at site SJ after spatfall in sumuicr<br />

1979 (1983 for St nihil ularia plana). The si/e classes vulnerable<br />

lo prcdaiion h\ Knol (See fable 2) are indicaied (horizontal grey<br />

fieldl. as well as ihe period during which Knot were present (vertical<br />

grey bars). Average sizes were calculated from the length lie<br />

queue) distribution* in the monthly samples (see 'Methods' i<br />

ten years. The contribution of the 1979 year class of<br />

Macoma lo the biomass harvestable by Knot is evi<strong>de</strong>nt:<br />

the harvestable <strong>food</strong> supply was highest alter<br />

four growing seasons <strong>and</strong> <strong>de</strong>creased thereafter because<br />

an increasing proportion had passed the critical size<br />

threshold of 16 mm.<br />

On some occasions. Macoma was the only prey<br />

species harvestable hv Knot for example in late summer<br />

of 1981 <strong>and</strong> 1983. Though Cerasto<strong>de</strong>rma were<br />

available in 1983. Knot ignored them, perhaps due to<br />

the thick shell (Zwarts & Blomen 1992). Macoma<br />

musl therefore have been the staple <strong>food</strong> for Knot that<br />

passed through ihe study area in late summer, unless<br />

the Mud Snail Peringia ulvae was taken as an alterna-<br />

295<br />

tive. This species usually occurred ai <strong>de</strong>nsities of<br />

40 000 to 50 000 nv'. though the summer of 1979 was<br />

an exception, when only low <strong>de</strong>nsities of 1000 m : occuned<br />

(Zwarts 19881*0 EJowevet direel observations<br />

<strong>and</strong> faecal analysis showed that Peringia were nol<br />

taken in 1979. 1981. 1983 or 1985. even though the)<br />

were abundant in three of ihe four years. In fact, the<br />

majority of Peringia in the study area were too small<br />

« 2 mm) to be profitable <strong>food</strong> items for Knot (Zwarts<br />

& Blomert 1992). The distribution paiiern of Knol<br />

over ihe feeding area was another indication lhat Knot<br />

did not feed on Peringia. This prey was superabundant<br />

at the sites situated above mean sea level <strong>and</strong> in areas<br />

where the clay content of the substrate was above 10%<br />

(Zwarts 1988b). However. Knot ignored these areas<br />

<strong>and</strong> were usually found on sites below mean sea level<br />

where the clay content of the substrate was less than<br />

This resulted in a negative relationship between<br />

<strong>de</strong>nsity of Knot <strong>and</strong> that of Peringia. Consi<strong>de</strong>ring all<br />

this information together, the conclusion is that Macoma<br />

was the main, <strong>and</strong> sometimes the only, prey for<br />

Knot in the study area. For thai reason, local <strong>and</strong> sea<br />

sonal variations only in Macoma are <strong>de</strong>scribed below.<br />

1977 78 79 80 81 82 83 84 85 86<br />

tig. 6. Biomass (g AFDW m -i ol live bivalve species M sik- \ m<br />

August from 1977 to 19X6. A selection has been ma<strong>de</strong> for the range<br />

of si/e classes barvulihlc b) Knol Calidris , annua (see fable 2).<br />

No correction has been ma<strong>de</strong> for <strong>de</strong>pth distribution of the prey.

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