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EMPAFISH Booklet no. 1 Ecological <strong>effects</strong> <strong>of</strong> Atlanto-Mediterranean MPAs in the EU<br />

1987 and 1989) and four years after it was in place (spring 1994) were<br />

compared. Sampling design was based on three depth strata (10-50 m, 51-<br />

100 m, 101-200 m); twenty-one and thirty hauls were made before and after<br />

the ban, respectively. Eleven target species (nine finfish and two<br />

cephalopods) as well as the total catch were used for comparisons. The total<br />

catch underwent an 8-fold increase in biomass after the four-year ban, and all<br />

the considered species underwent an increase, ranging from 1.2-fold for<br />

musky octopus (Eledone moschata) to 497-fold for gurnard (Lepidotrigla<br />

cavillone). The only decrease was for horned octopus (Eledone cirrhosa).<br />

Further studies showed that the demersal biomass remained at very high<br />

levels in the following years, in both inshore sandy <strong>areas</strong> and <strong>of</strong>fshore muddy<br />

<strong>areas</strong> (D’Anna et al. 2001; Pipitone et al. 2001; Pipitone et al. 2004). A model<br />

<strong>of</strong> distribution was set up using cellular automata for the red mullet<br />

(Badalamenti et al. 2002b).<br />

74<br />

o Trophodynamic changes<br />

The consequences for food-web structure <strong>of</strong> protecting <strong>marine</strong> communities<br />

from trawling have been explored in the Gulf (Badalamenti et al. 2000b;<br />

Badalamenti et al. 2002d). Using stable isotopes <strong>of</strong> carbon and nitrogen, our<br />

objectives were to see if mean trophic level and omnivory had increased after<br />

the ban in three <strong>of</strong> the most common fishery-target species, namely, the<br />

anglerfish Lophius budegassa, Mediterranean hake Merluccius merluccius, and<br />

red mullet Mullus barbatus. We compared size data from before and after the<br />

fishery closure, but we also compared recently derived data from outside and<br />

inside the closed area. In all three species δ13C and δ15N were found to differ<br />

markedly depending on fish size. δ13C was found to decrease in L. budegassa<br />

and M. merluccius but increase in M. barbatus with increasing fish length.<br />

δ15N increased in all three species, and this was thought to reflect feeding at<br />

increasingly higher trophic levels during the animals’ lives. Mean length, and<br />

therefore δ15N derived trophic level, increased after the trawl ban only in the<br />

anglerfish L. budegassa. Based on δ13C and δ15N data, none <strong>of</strong> the species<br />

became more or less omnivorous after the ban. After 9 years <strong>of</strong> no trawling,<br />

increases in numerical abundance were not accompanied by substantial sizerelated<br />

trophodynamic shifts in any <strong>of</strong> the three species <strong>of</strong> fish studied.<br />

The trophodynamics <strong>of</strong> three Mediterranean fishes robust to trawling<br />

disturbance was also investigated (Badalamenti et al., in press). Trawling has<br />

a significant effect on the structure <strong>of</strong> <strong>marine</strong> communities, yet the ubiquity <strong>of</strong><br />

trawling impacts makes the testing <strong>of</strong> spatial variation in such <strong>effects</strong> difficult.<br />

This study examines trawling impacts on fish trophodynamics by comparing<br />

trophodynamics in the Gulfs <strong>of</strong> Castellammare and Termini Imerese (northern<br />

Sicily) the first <strong>of</strong> which has had a large no-trawl area since 1990. Nitrogen<br />

and carbon stable isotope data were used to assess trophic levels and source<br />

<strong>of</strong> production supporting 3 demersal fish species (Mediterranean hake, red<br />

mullet and anglerfish). The exclusion <strong>of</strong> trawling has no <strong>ecological</strong>ly significant<br />

effect on fish trophic level at size and no systematic effect on the sources <strong>of</strong><br />

production supporting any species at the size sampled, thus discounting a<br />

large bottom-up influence on fish trophodynamics. Smaller scale variations<br />

(east/central/west sectors or depth strata) in δ13C isotopic signatures

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