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Proceedings of the Second Mediterranean Symposium on Marine

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PROCEEDINGS OF THE SECOND MEDITERRANEAN SYMPOSIUM ON MARINE VEGETATION (ATHENS, 12-13 DECEMBER 2003)<br />

158<br />

Under high wave energy, Cystoseira crinitophylla was dominant. This result is in<br />

accordance with previous observati<strong>on</strong>s from <str<strong>on</strong>g>the</str<strong>on</strong>g> Aegean (M<strong>on</strong>tesanto and Panayotidis,<br />

2000). The accompanying species are less abundant in Site 1 than in Site 2 probably<br />

because <str<strong>on</strong>g>the</str<strong>on</strong>g> high wave energy <str<strong>on</strong>g>of</str<strong>on</strong>g> Site 1 plays a limiting role <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> settlement <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

seas<strong>on</strong>al or opportunistic species. This lack <str<strong>on</strong>g>of</str<strong>on</strong>g> competiti<strong>on</strong> for C. crinitophylla in Site 1<br />

could also account for <str<strong>on</strong>g>the</str<strong>on</strong>g> highest coverage found in this site. The Cystoseira associati<strong>on</strong><br />

in Site 2 is more balanced. The moderate wave energy here is not a limiting factor for<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> settlement <str<strong>on</strong>g>of</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r species. This could explain <str<strong>on</strong>g>the</str<strong>on</strong>g> highest numbers <str<strong>on</strong>g>of</str<strong>on</strong>g> species and<br />

coverage for Rhodophyta and <str<strong>on</strong>g>the</str<strong>on</strong>g>refore <str<strong>on</strong>g>the</str<strong>on</strong>g> highest values <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> diversity and evenness<br />

indices. The numbers <str<strong>on</strong>g>of</str<strong>on</strong>g> species for Phaeophyceae were <str<strong>on</strong>g>the</str<strong>on</strong>g> highest in Site 2 as well.<br />

The hierarchical clustering that derived from <str<strong>on</strong>g>the</str<strong>on</strong>g> Bray-Curtis similarity matrix gave <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

dendrogram presented in Figure 1. The replicates <str<strong>on</strong>g>of</str<strong>on</strong>g> each site are grouped toge<str<strong>on</strong>g>the</str<strong>on</strong>g>r with<br />

high similarity values. Sites 1 and 2 (high wave energy) formed <strong>on</strong>e group (similarity<br />

50.76%). In <str<strong>on</strong>g>the</str<strong>on</strong>g> MDS plot (Figure 2), <str<strong>on</strong>g>the</str<strong>on</strong>g> Euclidean distances am<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> sites give us<br />

more informati<strong>on</strong>. Sites 1 and 2 are str<strong>on</strong>gly grouped toge<str<strong>on</strong>g>the</str<strong>on</strong>g>r.<br />

The Cystoseira associati<strong>on</strong>s in <str<strong>on</strong>g>the</str<strong>on</strong>g>se two sites c<strong>on</strong>struct typical aspects <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

Cystoseiretum crinitae Molinier 1958. This is a comm<strong>on</strong> associati<strong>on</strong> for moderately<br />

exposed coasts <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Mediterranean</str<strong>on</strong>g> with most frequent species C. crinita and<br />

C. compressa (Giaccc<strong>on</strong>e and Bruni, 1973). In <str<strong>on</strong>g>the</str<strong>on</strong>g> Aegean Sea, M<strong>on</strong>tesanto and<br />

Panayotidis (2000) have found that C. crinitophylla replaces C. crinita in highly or<br />

extremely exposed areas.<br />

C. foeniculacea f. tenuiramosa was <str<strong>on</strong>g>the</str<strong>on</strong>g> dominant species in <str<strong>on</strong>g>the</str<strong>on</strong>g> moderately sheltered<br />

site (Site 3). This species is obviously tolerant to <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>diti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> low wave energy. In<br />

additi<strong>on</strong>, <str<strong>on</strong>g>the</str<strong>on</strong>g> re-suspensi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> fine sand am<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> boulders could create high<br />

turbidity c<strong>on</strong>diti<strong>on</strong>s. Ercegovic (1952) suggested that C. foeniculacea f. tenuiramosa<br />

(=C. schiffneri f. tenuiramosa) is favored by c<strong>on</strong>diti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> low wave energy and<br />

transparency. The poor c<strong>on</strong>tributi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> accompanying species to this Cystoseira<br />

associati<strong>on</strong> and <str<strong>on</strong>g>the</str<strong>on</strong>g> very high coverage <str<strong>on</strong>g>of</str<strong>on</strong>g> C. foeniculacea f. tenuiramosa probably<br />

account for <str<strong>on</strong>g>the</str<strong>on</strong>g> lowest values <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> diversity and eveness indices here. C. foeniculacea<br />

f. tenuiramosa was <str<strong>on</strong>g>the</str<strong>on</strong>g> dominant species in <str<strong>on</strong>g>the</str<strong>on</strong>g> most sheltered site (Site 4). The lowest<br />

number <str<strong>on</strong>g>of</str<strong>on</strong>g> species and <str<strong>on</strong>g>the</str<strong>on</strong>g> lowest total coverage were found here as well.<br />

In <str<strong>on</strong>g>the</str<strong>on</strong>g> dendrogram <str<strong>on</strong>g>of</str<strong>on</strong>g> Fig. 1, Sites 3 and 4 (low wave energy) formed ano<str<strong>on</strong>g>the</str<strong>on</strong>g>r distinct<br />

group with lower similarity (38.39%) than Sites 1 and 2. In <str<strong>on</strong>g>the</str<strong>on</strong>g> MDS plot, Sites 3 and 4<br />

formed two distinct groups. The lower similarity here could be attributed to <str<strong>on</strong>g>the</str<strong>on</strong>g> presence<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> different epiphytic species in <str<strong>on</strong>g>the</str<strong>on</strong>g> two sites.<br />

Cystoseira schiffneri has a problematic tax<strong>on</strong>omy (Ercegovic, 1952). The associati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

C. foeniculacea and C. barbata were first described by Feldmann (1937) in protected<br />

areas where <str<strong>on</strong>g>the</str<strong>on</strong>g> hard substrate was occasi<strong>on</strong>ally covered by sediments. Athanassiadis<br />

(1987) also found C. foeniculacea in protected sites <str<strong>on</strong>g>of</str<strong>on</strong>g>ten. M<strong>on</strong>tesanto and Panayotidis<br />

(2000) found that C. foeniculacea (=C. scheffneri) accompanies C. crinita and C.<br />

compressa in sheltered or moderately exposed sites in <str<strong>on</strong>g>the</str<strong>on</strong>g> Aegean.<br />

The Cystoseira associati<strong>on</strong>s in <str<strong>on</strong>g>the</str<strong>on</strong>g>se two sites do not corresp<strong>on</strong>d clearly to any <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

associati<strong>on</strong>s described so far from <str<strong>on</strong>g>the</str<strong>on</strong>g> <str<strong>on</strong>g>Mediterranean</str<strong>on</strong>g>. Giacc<strong>on</strong>e and Martino (2000)

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