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A biological study of Durvillaea antarctica (Chamisso) Hariot and D ...

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191<br />

areal, but this was to be expected since the sites were cleared at<br />

different times during spring <strong>and</strong> summer, <strong>and</strong> differed slightly<br />

in terms <strong>of</strong> wave exposure <strong>and</strong> shore topography.<br />

These other seaweeds prevented dense recolonisation by<br />

DurviZlaea in the following winter, by occupying the predominantly<br />

bare areas. Area Sa (cleared October 1972: 28 m 2 ) contained only<br />

274 D. <strong>antarctica</strong> plants a year after clearing, <strong>and</strong> most <strong>of</strong> these were<br />

small specimens inadvertently missed during clearing in the previous<br />

October. However at least 50 plants were recruited in the 1973<br />

winter. Many <strong>of</strong> these were attached to the coralline turf. Codium<br />

adhaepena. mussels <strong>and</strong> even the shells <strong>of</strong> limpets. <strong>and</strong> were therefore<br />

easily detached during storms. Consequently most <strong>of</strong> the kelp plants<br />

present after 3~ years, were survivors,<strong>of</strong> those small specimens<br />

which escaped the clearing process. As the size <strong>of</strong> these plants<br />

increased, the area <strong>of</strong> coralline turf declined (Fig. 9.1, column 1).<br />

This may have been a result <strong>of</strong> shading <strong>and</strong>/or abrasion by the<br />

DurvilZaea fronds.<br />

The number <strong>of</strong> mussels (Perna canaliculus <strong>and</strong> to a lesser extent<br />

MYtiZia edulis aoteanus) exposed after the kelp was cut, declined<br />

over several months after clearing (Table 9.3). This applied<br />

particularly to those areas cleared during the spring <strong>and</strong> summer.<br />

On Area 9 (cleared 2 November 1974: 21.6 m 2 ) for example, all PePna<br />

disappeared within seven months. Originally many were loosely<br />

attached to the rock, <strong>and</strong> presumably a local increase in wave action<br />

following removal <strong>of</strong> the kelp, was the main cause. However I on th is<br />

same area, there was heavy settlement <strong>of</strong> MytiZis eduZie <strong>and</strong><br />

pulez 2 in the autumn <strong>and</strong> early winter after clearing (Fig. 9.1,<br />

column 3). No comparable recrui tJnent was found in adjacent control<br />

areas, so it seems likely that this was a direct effect <strong>of</strong> removing<br />

the kelp. Mortality <strong>of</strong> these small mussels was very high, however.<br />

Large rock slabs which were shifted about in the kelp zone during the<br />

winter <strong>of</strong> 1974 may have been partly responsible for this; but a more<br />

Ulva was never particularly common on Area Sa, but was important<br />

On three other areas. SpZanchnidium, Leathesia, Hetel'osiphcmia<br />

<strong>and</strong> RalfsM appeared on some areas <strong>and</strong> not on others.<br />

2 Formerly knOWn as Modiolus neozeZ<strong>and</strong>icus Ireda1e 1915.

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