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Proceedings of the Second Mediterranean Symposium on Marine

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J<strong>on</strong>ge et al., 2002). Nutrient c<strong>on</strong>centrati<strong>on</strong>s in water al<strong>on</strong>e are not indicative <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

eutrophicati<strong>on</strong> status, especially in shallow ecosystems, since primary producers<br />

assimilate <str<strong>on</strong>g>the</str<strong>on</strong>g> nutrients very efficiently and resp<strong>on</strong>d n<strong>on</strong>-linearly and self-accelerating<br />

when certain nutrient boundaries are crossed (Duarte, 1995). High organic c<strong>on</strong>tent <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

sediment, in additi<strong>on</strong>, could be toxic to marine angiosperms. Eutrophicati<strong>on</strong> is better<br />

indicated by its symptoms, which in <str<strong>on</strong>g>the</str<strong>on</strong>g> lago<strong>on</strong>s include shifts in species compositi<strong>on</strong><br />

from angiosperms to <str<strong>on</strong>g>the</str<strong>on</strong>g> dominance <str<strong>on</strong>g>of</str<strong>on</strong>g> opportunistic and <str<strong>on</strong>g>of</str<strong>on</strong>g>ten bloom forming<br />

seaweeds (Harlin, 1995; Schramm and Nienhuis, 1996). This predictable successi<strong>on</strong>al<br />

dynamic <str<strong>on</strong>g>of</str<strong>on</strong>g> macrophytes is induced also by o<str<strong>on</strong>g>the</str<strong>on</strong>g>r kinds <str<strong>on</strong>g>of</str<strong>on</strong>g> human disturbance, e.g.<br />

bottom-trawling, overharvesting <str<strong>on</strong>g>of</str<strong>on</strong>g> grazers or predators and is in accordance to classical<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g>ory <str<strong>on</strong>g>of</str<strong>on</strong>g> r- and K-selecti<strong>on</strong>.<br />

The use <str<strong>on</strong>g>of</str<strong>on</strong>g> benthic macrophytes as bioindicators <str<strong>on</strong>g>of</str<strong>on</strong>g> eutrophicati<strong>on</strong> and <str<strong>on</strong>g>of</str<strong>on</strong>g> water quality<br />

in general, several c<strong>on</strong>cepts, and numerical techniques (indicator taxa, diversity and biotic<br />

indices, multivariate tools) have been developed. Although compositi<strong>on</strong> analysis at<br />

species level is <str<strong>on</strong>g>of</str<strong>on</strong>g>ten measured, a more predictive science might be achieved by using<br />

appropriate functi<strong>on</strong>al classificati<strong>on</strong>s. They could reduce <str<strong>on</strong>g>the</str<strong>on</strong>g> apparent complexity <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

ecological systems and allow comparis<strong>on</strong>s between communities with little species<br />

overlap. Fur<str<strong>on</strong>g>the</str<strong>on</strong>g>rmore, <str<strong>on</strong>g>the</str<strong>on</strong>g>y could help to develop user-friendly protocols and costeffective<br />

m<strong>on</strong>itoring systems.<br />

The idea <str<strong>on</strong>g>of</str<strong>on</strong>g> defining plant types that are in some way related to ecosystem functi<strong>on</strong> is<br />

not new. For seaweeds, Littler and Littler (1980) have proposed functi<strong>on</strong>al groups, that<br />

irrespective <str<strong>on</strong>g>of</str<strong>on</strong>g> phylogeny, are similar in morphology and similar in <str<strong>on</strong>g>the</str<strong>on</strong>g>ir resp<strong>on</strong>ses to<br />

certain ecosystem functi<strong>on</strong>s, e.g. productivity, grazing. Orfanidis et al. (2001, 2003) have<br />

included seagrasses in this form-functi<strong>on</strong> system and <str<strong>on</strong>g>the</str<strong>on</strong>g>n have used it to divide <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

benthic macrophytes in two differently resp<strong>on</strong>ding to envir<strong>on</strong>mental disturbance groups,<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> late-successi<strong>on</strong>al (K-selecti<strong>on</strong>) and <str<strong>on</strong>g>the</str<strong>on</strong>g> opportunistic (r-selecti<strong>on</strong>). The result <str<strong>on</strong>g>of</str<strong>on</strong>g> this<br />

approach, which explains general macrophyte patterns across a polluti<strong>on</strong> gradient mainly<br />

through <str<strong>on</strong>g>the</str<strong>on</strong>g>ir competitive abilities (Sommer and Worm, 2002), was <str<strong>on</strong>g>the</str<strong>on</strong>g> Ecological<br />

evaluati<strong>on</strong>-EEI index.<br />

In this study we m<strong>on</strong>itored <str<strong>on</strong>g>the</str<strong>on</strong>g> marine benthic macrophytes across an eutrophicati<strong>on</strong><br />

gradient <str<strong>on</strong>g>of</str<strong>on</strong>g> selected Eastern Maced<strong>on</strong>ian & Thrace lago<strong>on</strong>s. The aims were (1) to select<br />

reliably interpretable signals <str<strong>on</strong>g>of</str<strong>on</strong>g> macrophyte resp<strong>on</strong>ses by critically comparing different<br />

parameters <str<strong>on</strong>g>of</str<strong>on</strong>g> compositi<strong>on</strong> analysis, based at species- and functi<strong>on</strong>al group-level, and <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

biotic index EEI, (2) to suggest user-friendly protocols for a cost-effective m<strong>on</strong>itoring<br />

program, e.g. WFD.<br />

MATERIAL AND METHODS<br />

Study area. The studied lago<strong>on</strong>s bel<strong>on</strong>g to <str<strong>on</strong>g>the</str<strong>on</strong>g> Nestos River and Vist<strong>on</strong>ida estuarine<br />

system catchments (Fig. 1). They are protected by Ramsar c<strong>on</strong>venti<strong>on</strong> and were<br />

suggested to be included in <str<strong>on</strong>g>the</str<strong>on</strong>g> European Natura 2000 network. Traditi<strong>on</strong>al fish<br />

aquaculture (mesh frames, stati<strong>on</strong>ary entrapment system) is <str<strong>on</strong>g>the</str<strong>on</strong>g> main commercial use <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> lago<strong>on</strong>s. The main nutrient sources <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> Nestos lago<strong>on</strong>s are agricultural run-<str<strong>on</strong>g>of</str<strong>on</strong>g>fs<br />

ACTES DU DEUXIEME SYMPOSIUM MEDITERRANEEN SUR LA VEGETATION MARINE (ATHENES, 12-13 DECEMBRE 2003)<br />

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