“…Glasby & Connell, 2001;Firth et al, 2016b;Ushiama et al, 2016), herbivory (Forrest et al, 2013;Ferrario et al, 2016), roughness and nature of building materials (e.g. Coombes et al, 2015;Cacabelos et al, 2016;Sempere-Valverde et al, 2018). The sampling design considered in our study eliminated potential confounding effects due to some factors (e.g.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…All in all, and given that the sampled artificial structures in our study were adjacent to natural hard substrates, thus facilitating the potential nourishment of rip-raps (Gacia et al, 2007), it is improbable that poor larval or propagules dispersal limits the establishment of assemblages on rip-raps. On the other hand, their settlement could be affected by other factors such as nature of building materials and roughness (Coombes et al, 2015;Ido & Shimrit, 2015;Sempere-Valverde et al, 2018) or ecological processes, such as grazing, predation and competition (Foster et al, 2003;Bulleri, 2005;Marzinelli et al, 2011;Ferrario et al, 2017). Besides the differences in assemblage composition and diversity, the cover of habitat-forming arborescent macroalgae was significantly lower in rip-raps, thus potentially generating differences in ecosystem functioning.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…We suggest that future constructions should apply ecological criteria considering various materials (e.g. Sempere-Valverde et al, 2018) and novel designs (Ostalé-Valriberas et al, 2018) which could match the particular scenario of the Cretan coast. Further research for the ecological characterization of these structures is critical in order to improve our knowledge in support of better management practices, under the framework of green engineering, in coastal and marine infrastructure of the Eastern Mediterranean Sea.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…Perkol-Finkel & Benayahu, 2004;Lam et al, 2009;Loke et al, 2015;Mercader et al, 2017), nature of building materials (e.g. Coombes et al, 2015;Sempere-Valverde et al, 2018), surface inclination and orientation (e.g. Moreira et al, 2006;Chapman & Underwood, 2011) and even differential grazing pressure between artificial and natural habitats (Ferrario et al, 2016).…”
Artificial structures cover a considerable part of the Mediterranean coasts. In the Aegean Sea, most studies related to artificial structures have focused in vagile fauna on harbors and marinas but little attention has been given to the sessile biota on coastal defense structures. The aim of this work was to describe for the first time the shallow sublittoral sessile benthos on coastal defense structures in Crete (Eastern Mediterranean Sea) in order to identify potential differences in comparison to natural rocky substrates, adopting both a taxonomic and functional (i.e. macroalgal structural complexity) approach. Three shallow (1-3 m) localities were studied in the north coast and three in the south coast of the island (six localities in total). At each locality, two types of hard substrate were selected: an artificial coastal defense structure (rip-rap) and the nearest natural rocky substrates. The percent cover of sessile taxa was calculated using random points counts over photoquadrats (20 x 20 cm). The structure of the assemblage differed between artificial and natural habitats. Values of Shannon-Wiener’s diversity index and number of taxa were higher in natural substrates. In addition, cover of arborescent macroalgae was lower on artificial substrates. In conclusion, rip-raps do not function as surrogates of natural hard substrates in the study area since their shallow subtidal assemblages differ in terms of community structure, diversity and functionality. The deficient performance of such artificial structures could be attributed to the combined effects of abiotic factors and biotic processes, including substrate nature and roughness as well as differential grazing pressure.
“…Glasby & Connell, 2001;Firth et al, 2016b;Ushiama et al, 2016), herbivory (Forrest et al, 2013;Ferrario et al, 2016), roughness and nature of building materials (e.g. Coombes et al, 2015;Cacabelos et al, 2016;Sempere-Valverde et al, 2018). The sampling design considered in our study eliminated potential confounding effects due to some factors (e.g.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…All in all, and given that the sampled artificial structures in our study were adjacent to natural hard substrates, thus facilitating the potential nourishment of rip-raps (Gacia et al, 2007), it is improbable that poor larval or propagules dispersal limits the establishment of assemblages on rip-raps. On the other hand, their settlement could be affected by other factors such as nature of building materials and roughness (Coombes et al, 2015;Ido & Shimrit, 2015;Sempere-Valverde et al, 2018) or ecological processes, such as grazing, predation and competition (Foster et al, 2003;Bulleri, 2005;Marzinelli et al, 2011;Ferrario et al, 2017). Besides the differences in assemblage composition and diversity, the cover of habitat-forming arborescent macroalgae was significantly lower in rip-raps, thus potentially generating differences in ecosystem functioning.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…We suggest that future constructions should apply ecological criteria considering various materials (e.g. Sempere-Valverde et al, 2018) and novel designs (Ostalé-Valriberas et al, 2018) which could match the particular scenario of the Cretan coast. Further research for the ecological characterization of these structures is critical in order to improve our knowledge in support of better management practices, under the framework of green engineering, in coastal and marine infrastructure of the Eastern Mediterranean Sea.…”
Section: Number Of Taxa (S) Shannon-wiener Diversity (H') Pielou's Evmentioning
confidence: 99%
“…Perkol-Finkel & Benayahu, 2004;Lam et al, 2009;Loke et al, 2015;Mercader et al, 2017), nature of building materials (e.g. Coombes et al, 2015;Sempere-Valverde et al, 2018), surface inclination and orientation (e.g. Moreira et al, 2006;Chapman & Underwood, 2011) and even differential grazing pressure between artificial and natural habitats (Ferrario et al, 2016).…”
Artificial structures cover a considerable part of the Mediterranean coasts. In the Aegean Sea, most studies related to artificial structures have focused in vagile fauna on harbors and marinas but little attention has been given to the sessile biota on coastal defense structures. The aim of this work was to describe for the first time the shallow sublittoral sessile benthos on coastal defense structures in Crete (Eastern Mediterranean Sea) in order to identify potential differences in comparison to natural rocky substrates, adopting both a taxonomic and functional (i.e. macroalgal structural complexity) approach. Three shallow (1-3 m) localities were studied in the north coast and three in the south coast of the island (six localities in total). At each locality, two types of hard substrate were selected: an artificial coastal defense structure (rip-rap) and the nearest natural rocky substrates. The percent cover of sessile taxa was calculated using random points counts over photoquadrats (20 x 20 cm). The structure of the assemblage differed between artificial and natural habitats. Values of Shannon-Wiener’s diversity index and number of taxa were higher in natural substrates. In addition, cover of arborescent macroalgae was lower on artificial substrates. In conclusion, rip-raps do not function as surrogates of natural hard substrates in the study area since their shallow subtidal assemblages differ in terms of community structure, diversity and functionality. The deficient performance of such artificial structures could be attributed to the combined effects of abiotic factors and biotic processes, including substrate nature and roughness as well as differential grazing pressure.
“…plastics, ropes, and concrete), which often lack the features that contribute to increasing microhabitat diversity in natural areas (i.e. roughness and spatial heterogeneity) (Bulleri & Chapman, 2010;Ostalé-Valriberas et al, 2018;Sempere-Valverde et al, 2018). Floating structures such as pontoons may also increase NIS abundance when compared with non-floating substrata (Megina et al, 2016).…”
The Mediterranean Sea is a marine biodiversity hotspot under threat. One of the major impacts on its biological resources and services comes from the invasiveness of non-indigenous species (NIS). Nevertheless, NIS monitoring programs in the south basin of the Mediterranean Sea are in an early implementation stage. This study aims to describe NIS and cryptogenic species distribution in Monastir Bay (Tunisia) and to identify risk areas for the introduction and spread of invasive species, providing a baseline for future monitoring programs. To this end, a series of Rapid Assessment Surveys were carried out to identify NIS and cryptogenic species in one marina, five fishing ports, two aquaculture farms and the Special Conservation Area of the Kuriat islands. 24 species were found, of which 11 constitute new records for Monastir Bay, which represent a 33.3% of the total NIS reported in this Bay. Assemblages differed between substrata types, being NIS more abundant in artificial than in natural substrata. Regarding locations, Cap Monastir Marina was the most invaded site, the most transited by vessels and the only one visited by international sailing. Hence, this marina constitutes the main risk area to be monitored, although the fishing ports and fishing farms in the semi-enclosed coastal lagoon of Monastir Bay can also be considered as risk areas. Nevertheless, more research effort is needed in Monastir Bay in order to update the records of NIS and cryptogenic species and increase insight on the ecological evolution of these species and their related impacts on natural communities and marine resources.
Mollusc communities are getting endangered in the aftermath of urban sprawl because artificial structures do not surrogate natural substrates. In this study, we compared the diversity, community and trophic arrangements of molluscs among different models of artificial substrate and their adjacent natural rock, to detect relationships between some abiotic variables and the mollusc communities. Complexity, chemical composition and age were tested as potential drivers of the community. Diversity, community and trophic structure differed between natural and artificial substrates. Complexity at the scale of cm was detected as the most important factor driving the community structure. In addition, a chemical composition based on silica and/or scarce calcium carbonates seems to be relevant for molluscs, as well as for the secondary substrate where they inhabit. However, age did not seem to be a driving factor. Among the different artificial structures, macroscale complexity was detected as the main factor diverging a drastically poor community at seawall from other artificial structures. In this context, macro and microscale complexity, chemical composition and mineral type are variables to consider in future designs of artificial substrates.
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