Page 2 - Mannino-Balistreri_2018
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2      A. M. MANNINO AND P. BALISTRERI

               Since frontiers do not exist in the sea, biological inva-  Mediterranean communities (Boudouresque et al. 1995;
             sions may severely affect MPAs, whose major aim is bio-  Klein and Verlaque 2008; Papini, Mosti, and Santosuosso
             diversity conservation, because they are also located in   2013; Katsanevakis et al. 2014). This species, first recorded
             proximity to ports and marinas or are frequently used   in Italy in 1993 at Baia di San Panagia (Sicily) and at the
             by small recreational or fishing boats as well as tourists.   Island of Lampedusa (Alongi et al. 1993), is currently pres-
             Despite the availability of a large amount of information   ent around almost all the Mediterranean Sea.
             on MPAs, the effects of MPAs on IAS has been poorly   We report our experience of citizen science in the Egadi
             studied (Burfeind et al. 2013; Ardura et al. 2016; Giakoumi   Islands MPA with the project ‘Caulerpa cylindracea –
             et al. 2016; Giakoumi and Pey 2017). It therefore remains   Egadi Islands’, aimed at monitoring the spread dynamics
             doubtful if MPAs are able to resist IAS, due to the high spe-  of C. cylindracea within the Egadi Islands MPA.
             cies richness conferring them an ‘invasion resistance’, or
             instead may favour their introduction and spread through   Material and methods
             tourism activities, which increase disturbance and vectors
             (boat anchors, diving, etc.) (Giakoumi and Pey 2017).  The Egadi Islands MPA (Aegadian archipelago), instituted
               To reduce the risk of future IAS introduction and to   in 1991, is the largest Italian MPA. This small archipelago,
             better understand their invasive potential and spread   located approximately 7–9 km from the western coast of
             dynamics, monitoring and surveillance plans are    Sicily (Italy, Tyrrhenian Sea), is composed of three main
             required. The creation of permanent alarm systems and   islands (Favignana 37°56′00′′ N, 12°19′00′′ E; Marettimo
             public awareness campaigns might be effective tools in   37°58′00′′ N, 12°03′00′′ E; Levanzo 38°00′00′′ N, 12°20′00′′
             the management of IAS introductions. In this regard,   E) and a few small islets (Galeotta 37°54′43′′ N, 12°17′55′′
             MPAs, where the effects of NIS invasion can be studied   E; Galera 37°54′51′′ N, 12°17′24′′ E; Preveto 37°54′51.68′′
             and management strategies can be developed, might play   N, 12°18′7.57′′ E; Formica 37°59′21′′ N, 12°25′31′′ E;
             an important role as ‘sentinel systems’. Recently, an IAS   Maraone 37°59′23′′ N, 12°24′51′′ E) (Figure 1).
             strategy for the MedPAN Network, aiming to promote   The project ‘Caulerpa  cylindracea – Egadi Islands’,
             the establishment, the operation and the sustainability of   addressed to different groups of volunteers (students,
             a Mediterranean network of MPAs, has been developed.   tourists, divers, underwater photographers, amateurs and
             The strategy intends to assist MPAs for invasive species   fishermen), was based on the collection of data (place,
             management.                                        date, depth, substrate coverage %) and photos concerning
               To plan effective management and conservation strat-  the occurrence of C. cylindracea within the MPA. Only
             egies, reliable data on distribution and spread dynamics   data validated by the scientific team of the project were
             of IAS are essential. Since intensive monitoring programs   gathered in the database.
             could be very expensive, citizen science, involving citizens
             (e.g. tourists, fishermen, divers) in the collection of data,   Results and discussion
             could be a useful tool for providing data on IAS that would
             otherwise be impossible to collect because of limitations   The project was presented during the International
             on time and resources. Of course, all these data are reli-  Congress GeoSub2016 (Mannino, Donati, and Balistreri
             able only if they are scientifically validated. The number   2016). The Facebook page of the project registered numer-
             of citizen science projects (e.g. ‘Seawatchers’, available at   ous followers (3000 only in the last month). In all we gath-
             http://www.observadoresdelmar.es/?idioma=en, ‘Aliens in   ered 156 sightings mainly recorded by citizens (Figure 2).
             the sea’ available at the Facebook page: Progetto ‘Aliens in   The alga was reported from all the three main islands even
             the sea’, ‘Spot the Alien Fish’, available at https://www.face-  though the majority of the records were from Favignana
             book.com/aliensmalta, and MedMIS, a new IUCN app   (Figure 1). It was found in different habitats, between 0
             for marine invasive species in Mediterranean MPAs) has   and 40 m depth, mainly on rock, rock with sediment and
             rapidly and enormously increased in recent years (Conrad   sand (Figures 3 and 4). Useful information on the behav-
             and Hilchey 2011), thanks also to the wide availability   iour strategies of the alga was also gathered, e.g. the abil-
             of mobile technologies and internet access that enable   ity of the stolons to create bridges in order to reach new
             an easy and cheap way to communicate, share and inter-  areas for the anchorage and the strength of the anchorage
             change data. Currently, citizen science has been widely   due to the high number of rhizoids (Figure 4(d)). These
             recognised as an effective tool to expand the scale of NIS   strategies allow C. cylindracea to spread rapidly, forming
             data collection and monitoring.                    compact multi-layered mats able to trap the sediment that
               Among IAS, Caulerpa cylindracea Sonder, introduced   negatively affect the native macroalgal assemblages (Klein
             from Australia and New Caledonia (Belton et al. 2014),   and Verlaque 2008; Holmer et al. 2009; Matijević et al.
             has raised serious concern due to its ascertained impact on   2013). A low diversity was observed in areas colonised by
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