Artificial coastal structures, such as seawalls, breakwaters, and groins, can exert various impacts on the fish communities in the nearby regions. This study focuses on assessing the ecological effects of coastal infrastructure on marine environments, by comparing, at different seasons, the habitat complexity and heterogeneity, as well as their effects on fish assemblages, between the artificial habitat created with the intention of constructing a marina (Puerto Amor) and the natural habitats surrounding the Cabo de la Huerta area in Alicante (Spain). Employing an asymmetric design and examining two temporal and spatial scales, we utilized visual censuses in snorkeling to gauge the abundance and size of fish species, alongside various parameters related to habitat complexity and heterogeneity. The overarching hypothesis is that fish populations associated with artificial habitats will differ in terms of abundance, biomass, species richness, and diversity compared to fish populations associated with natural habitats, due to changes in complexity and heterogeneity. The findings indicate a shift in fish assemblages; for example, the family Labridae showed differences between the two habitat types for several species. These changes were due to the influences of the Posidonia oceanica meadow and algae like Jania rubens; being influenced by biological variables such as Ellisolandia elongata, Oculina patagonica, and Sarcotragus spinosulus; as well as physical variables such as stones, gravel, and blocks. While there is evidence of alteration in fish assemblages due to changes in habitat structure, there is also an increase in richness (9 species/m2) and total abundance and biomass (1000 ind./m2 and 1700 g/m2, respectively) in the artificial habitat. Multivariate analyses reveal that the fish community in Puerto Amor is less homogeneous than the one in the natural habitat. However, these analyses also indicate an overlap between the communities of both habitats, suggesting substantial similarity despite the noted differences. Consequently, although the habitat alteration has impacted fish populations, it has not diminished abundance, biomass, or species richness. In conclusion, the artificial rocky habitat resulting from the construction attempt at Puerto Amor harbor has fish populations with ecological significance and its removal could lead to undesirable impacts in the area, as the fish assemblages have become well established.
Posidonia oceanica seagrass meadows have been degraded in the Mediterranean Sea by trawling. To reduce this impact, antitrawling artificial reefs have been deployed. The introduction of artificial structures on seagrass meadows, however, could potentially change the composition of fishes. Using visual techniques, we examined changes in fish assemblage and density of key species by comparing fish abundances at four seagrass sites with and without artificial reef blocks in El Campello (Alicante), southeastern Spain, between October 1992 and August 1995. The fish assemblage on plots with artificial reefs changed substantially a year after their installation in October 1992. Differences in fish abundance (total counts of 6,692 fish on artificial reefs and 3,565 fish on Posidonia) and in species richness (41 species on artificial reefs and 29 on Posidonia) were found. The abundance of key species were quite different between habitats. Diplodus vulgaris and Chromis chromis were most abundant in all samples, whereas Oblada melanura recruited to the artificial reefs during winter 1994. Two species, Apogon imberbis and Sciaena umbra were found at all times on artificial reefs but were not present in P. oceanica plots. The antitrawling artificial reefs influenced the spatial distribution of fishes on a scale of tens to hundreds of meters but did not affect the overall Posidonia fish assemblage. Antitrawling artificial reefs protect seagrass from trawling and had little overall effect on seagrass fish assemblages in areas away from the artificial reefs.
Farm sabotage can cause massive fish escape events with significant ecological and socio-economic risks. This study examined the fate of Mediterranean seabass Dicentrarchus labrax escapees following a large-scale escape event caused by sabotage in the Western Mediterranean Sea. We monitored the escapee density and size structure over 3 mo after the escape at increasing distances from the escape point, up to 45 km away. Fish density adjacent to the escape location 5 d after the sabotage was, on average, 114 ± 44.7 (SE) fish per 100 m 2 . Our analyses showed that fish density decreased by 17% for every km away from the location, dropping to 2 and 1% after 1 and 2 mo, respectively, following the escape event. As escapee density declined throughout time and space, the size distribution of seabass shifted towards larger sizes. The rapid decrease in fish densities highlights the need for contingency plans focusing on fishing efforts in the coastal areas near the escape location (<20 km) within the first 24 h. These results are paramount to mitigating the risks associated with escape events cost-effectively. We emphasise the importance of sabotage prevention measures, such as security systems that can quickly detect intruders and trigger an immediate response to deter them. Additionally, enforcing appropriate sanctions based on the severity of the damage caused could help to discourage future sabotage attempts.