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

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known siphon weight <strong>and</strong> burying <strong>de</strong>pth. Zwarts<br />

(1986i showed that the burying <strong>de</strong>pth oi Scrobicularia<br />

was not only a function of siphon weight, but also of<br />

body condition. Using the equations from Fig. 8. the<br />

average feeding radius may be estimated for individuals<br />

living at different <strong>de</strong>pths (Fig. 10). All animals ha\ -<br />

ing a body weight > 10% above the average, are able to<br />

take no risks <strong>and</strong> live in a <strong>de</strong>pth refuge beneath the upper<br />

6 cm of the substrate exploited by the main predator,<br />

the Oystercatcher Haematopus oslralegus (Wanink<br />

& Zwarts 1985). This means that in animals with<br />

a short siphon but reasonable body condition, the<br />

entire siphon length is used for living as <strong>de</strong>eply as possible<br />

so that there is no extra opportunity for <strong>de</strong>posit<br />

feeding on the surface. However, animals with a relatively<br />

low body weight have fewer reserves, making it<br />

more important for them lo avoid further starvation,<br />

<strong>and</strong> so they accept a larger predation risk by living<br />

nearer to the surface. These animals extend about 40%<br />

of the siphon length over the surface to feed, even<br />

when the siphons are quite short. However, as Fig. 10<br />

shows, if the siphon is very short, the bivalves put<br />

mote emphasis on predator protection than on <strong>food</strong> input,<br />

presumably to avoid the extremely high predation<br />

risk associated with living at a very shallow <strong>de</strong>pth<br />

(Wanink & Zwarts 1985). This supports the suggestion<br />

of Zwarts (1986) that the choice of the burying <strong>de</strong>pth<br />

in <strong>de</strong>posit-feeding bivalves is the result of a tra<strong>de</strong>-off<br />

between predator avoidance <strong>and</strong> feeding. The observation<br />

that the feeding radius becomes smaller <strong>and</strong> burying<br />

<strong>de</strong>pth greater in Macoma whose feeding circumstances<br />

improve (Lin & Hines 1994). indicates that<br />

burying <strong>de</strong>pth is the outcome of conflicting <strong>de</strong>m<strong>and</strong>s<br />

<strong>and</strong> that, un<strong>de</strong>r each set of conditions, an optimum can<br />

be <strong>de</strong>fined.<br />

An interspecific comparison between siphon<br />

liiiLii h <strong>and</strong> siphon weight<br />

The average siphon weight oi Scrobicularia (35 mm)<br />

amounts to 10 mg. corresponding to an average siphon<br />

length of 10 to 11 cm (Fig. 8A). Scrobicularia live in<br />

winter at an average burying <strong>de</strong>pth of 10 cm (Fig. 5 in<br />

Zwarts & Wanink 1989. 1993). so that they should just<br />

be able to reach the surface. On average. Macoma (15<br />

mm) extend <strong>their</strong> siphon 5 cm (Fig. 9B). <strong>and</strong> they live<br />

al an average <strong>de</strong>pth of 5 cm in winter (Fig. 4 in Zw arts<br />

& Wanink 1989). As in Scrobicularia. the estimated<br />

FEEDING RADIUS. BURYING DEPTH AND SIPHON SIZE<br />

126<br />

overage siphon length agrees closely with the measured<br />

average burying <strong>de</strong>pth in winter. This means thai<br />

both bivalve species increase <strong>their</strong> <strong>de</strong>pth in winter just<br />

to the point at which, on average, they are able to reach<br />

the surface (o acquire oxygen from above the black<br />

mud where they live. This implies that they do not feed<br />

on the surface. Both species live at shallower <strong>de</strong>pths in<br />

summer (Zwarts & Wanink 1989. 1993). At this time<br />

of the year, the predicted feeding radius is on average<br />

4 cm in Scrobicularia (the gap between the two lines in<br />

Fig. 8) <strong>and</strong> 2 to 3 cm in Macoma. which is similar to<br />

the observed range in both species. These agreements<br />

between predicted <strong>and</strong> observed burying <strong>de</strong>pths in<br />

winter <strong>and</strong> surface radius in summer suggest thai the<br />

predictions of siphon length on ihe basis of siphon<br />

weight work out well.<br />

Scrobicularia live in winter at twice the <strong>de</strong>pth of<br />

Macoma <strong>and</strong> also invest, relative to total body weighl.<br />

Iwice as much material in <strong>their</strong> inhalant siphon (Figs. 8<br />

<strong>and</strong> 9). Siphon weight is 5 f f of the total bodv weight in<br />

Scrobicularia (35 mm), but this is only 2 to 3% in Macoma<br />

(15 mm) (Fig. 12 in Zwarts & Wanink 1989).<br />

The weight per cm of exten<strong>de</strong>d siphon (1.0 mg cm' 1 in<br />

Scrobicularia <strong>and</strong> 0.2 mg cm* 1 in Macoma. on average)<br />

is in both species equivalent to 0.5 to 0.6% of the<br />

total body weight (224 mg in Scrobicularia <strong>and</strong> 33.8<br />

mg in Macoma. on average: Fig. 8 in Zwarts 1991).<br />

The closely-related Tellina tenuis is even smaller than<br />

Macoma (flesh content 15 to 25 mg), yet lives as<br />

<strong>de</strong>eply as Scrobicularia (10 cm) (Trevellion 1971). Its<br />

siphon weight of I to 2 mg (Trevellion 1971) is relatively<br />

high, representing 7.5% of the total body weight.<br />

However, the weighl per cm exten<strong>de</strong>d siphon is similar<br />

to Scrobicularia <strong>and</strong> Macoma if we assume that the<br />

siphon is protru<strong>de</strong>d I to 3 cm above the surface. Body<br />

<strong>and</strong> siphon weight <strong>and</strong> burying <strong>de</strong>pth have also been<br />

<strong>de</strong>termined of a filter-feeding bivalve. Cerasto<strong>de</strong>rma<br />

edule (Zwarts & Wanink 1989). This species lives 1.5<br />

cm below ihe surface <strong>and</strong> the weight of the inhalant<br />

siphon is 1% of total body weight. Since the siphon is<br />

exten<strong>de</strong>d only a short distance above the surface, the<br />

investment per cm siphon lengih is slightly below<br />

0.7% of the total body weight. Comparable data for<br />

more bivalves are nee<strong>de</strong>d to know whether the apparent<br />

ten<strong>de</strong>ncy for siphon investment to equal about<br />

0.6% per cm extension, in<strong>de</strong>pen<strong>de</strong>nt of size, is a general<br />

phenomenon in bivalves.

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