Figures
Abstract
Fish assemblages associated with 14 marine caves and adjacent external rocky reefs were investigated at four Marine Protected Areas (MPAs) along the coasts of Italy. Within the caves sampling was carried out in different sub-habitats: walls, ceilings, bottoms and ends of caves. On the whole, 38 species were recorded inside the 14 caves investigated. Eighteen species were exclusively found inside the caves: they were mainly represented by speleophilic (i.e. species preferentially or exclusively inhabiting caves) gobids (e.g. Didogobius splechtnai) and nocturnal species (e.g. Conger conger). Forty-one species were censused outside, 20 of which were shared with cave habitats. Apogon imberbis was the most common fish found in all 14 caves investigated, followed by Thorogobius ephippiatus (recorded in 13 caves), and Diplodus vulgaris and Scorpaena notata (both censused in 12 caves). Distinct fish assemblages were found between external rocky reefs and the different cave sub-habitats. New data on the distribution of some speleophilic gobids were collected, showing the existence of a pool of species shared by marine caves on a large scale (i.e. hundreds of km). Considering the uniqueness of cave fishes (18 exclusive species and different assemblage structures), the inclusion of marine caves among the habitats routinely investigated for fish biodiversity monitoring could facilitate the achievement of more comprehensive inventories. Due to their contribution to local species diversity and the shelter they provide to species valuable for conservation, marine caves should be prioritized for their inclusion not only within future MPAs through the Mediterranean Sea, but also into larger management spatial planning.
Citation: Bussotti S, Di Franco A, Francour P, Guidetti P (2015) Fish Assemblages of Mediterranean Marine Caves. PLoS ONE 10(4): e0122632. https://doi.org/10.1371/journal.pone.0122632
Academic Editor: Carlo Nike Bianchi, Università di Genova, ITALY
Received: December 18, 2014; Accepted: February 23, 2015; Published: April 13, 2015
Copyright: © 2015 Bussotti et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All data are included within the Supporting Information files.
Funding: The study was funded by the 'Ministero dell’Ambiente e della Tutela del Territorio e del Mare' (Italy) in the framework of the project 'Studio degli ambienti di grotte marine sommerse (codice Habitat 8330) nelle Aree Marine Protette di Pelagie, Plemmirio e Capo Caccia' and by TOTAL Foundation (France). The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Along the coasts of the Mediterranean Sea, especially in rocky limestone areas subject to karstic dissolution, submerged marine caves are widespread and mostly unexplored natural habitats [1]. Because of the intrinsic variability and complexity of submerged marine cave systems, it is difficult to formally define them. In the Mediterranean context, some authors [2], [3] provided an operative and general definition: a “marine cave” is a cavity of various origin, completely or partially submerged, characterised by 1) a ratio between ‘overall internal volume/surface of the opening’ higher than 1, and 2) a width of the opening that should not exceed the mean width inside.
Due to their special ecological conditions inside, e.g. in terms of gradients of light intensity, water motion and distribution of trophic resources [2], [3], marine caves in the Mediterranean host unique and fragile biological communities (see e.g. [1], [4], [5–7]). Considering that benthic organisms living in coastal rocky habitats outside the caves usually compete for space occupation [8], [9], the presence of caves can also be seen as increasing the availability of coastal rocky substrates (see [10]).
Several coastal fishes can be found inside marine caves in the Mediterranean Sea. They encompass 1) species exclusively associated with marine caves (i.e. speleophilic), 2) nocturnal species (normally remaining within refuges during the day but moving outside at night), 3) species typical of cryptic habitats (including caves but also relatively small holes, under stones and crevices in the bedrock outside the caves), and 4) nectobenthic species generally associated with rocky reefs that can be found occasionally within caves, often in their initial portions [2], [10–17]. Cryptic habitats, including marine caves, have also been reported to host lessepsian fishes (Red Sea and Indo-Pacific species that enter the Mediterranean through the Suez Canal). It is case, for instance, of the dusky sweeper, Pempheris rhomboidea, in the Eastern Mediterranean, whose taxonomic aspects have been recently elucidated in [18]. Along some stretches of Turkish coast (e.g. around Antalya, Mediterranean Sea; Guidetti, pers. obs., but see also [19]), P. rhomboidea occupies the same micro-habitats (i.e. small crevices, under stones and boulders) that Apogon imberbis (native fish) generally occupies in the western Mediterranean, where it is very common [20]. In the case of further spreading of P. rhomboidea westwards it is reasonable to hypothesize competition between the alien and the native fish for the occupation of caves and any other cryptic habitat [21].
All the above issues suggest that assessing the fish fauna of marine caves may have important implications for conservation and management, including the monitoring of the spreading of some potentially invasive species.
The available scientific literature dealing with fish inhabiting Mediterranean marine caves is mainly focused on micro-habitat requirements of small cryptic species (e.g. [13], [22–25]). Abel [11], first, defined the ‘cave habitat’ for fishes as any ‘hole’ able to host the body of a fish, thus relating the spatial extension of the ‘cave’ to the body size of fish. He also created the term “cave in cave” for the specific territories of the speleophilic Microlipophrys nigriceps inhabiting piddock holes (small holes produced by boring mollusks within caves). Zander [22] used the term ‘mesolithion’ to define the cavity systems characterized by a decrease of light and water movement, independently of cavity size. Patzner [24] distinguished different cryptic habitats for coastal fishes, i.e. cavities (with cavity depth/length smaller that height/width, and low light levels) and caves (whose depth/length always exceeds height/width of the entrance, scarcely lighted to completely dark, sometimes with bottoms covered with fine sediment).
More active swimming fishes, such as sea breams, mullets, small serranids, may inhabit marine caves. However, they have in general received little attention compared with small cryptic species. Similarly, macroscopic cave features potentially affecting presence and distribution of fish (e.g. topography, presence/absence of secondary openings, presence/absence of air chambers, freshwater inputs, wave exposure, dimensions and number of tunnels and/or chambers, rocky or muddy bottom, etc.) have seldom been quantitatively assessed. Arko-Pijevac et al. [14] noted that the bulk of studies carried out on Mediterranean fish cave assemblages were done mostly 1) on small-sized sedentary cryptic fishes, and 2) within caves of limited size (<10 m long) often without reporting specific information on cave dimensions, structure and variety of sub-habitat types inside (e.g. openings, obscure ends, ceiling).
A more exhaustive description of cave habitats should take into account a number of features and scales potentially relevant in structuring fish assemblages. However, morphological features of marine caves are extremely variable from cave to cave (see [26]). This may have a strong influence on the diversity and structure of fish assemblages hosted inside, and can make it quite difficult to apply standardized approaches (i.e. formal sampling designs) to collect field data.
In recent years some studies on fish assemblages associated with Mediterranean marine caves were done following guidelines that formally satisfied fundamental aspects of sampling design theory applied to ecological studies (see e.g. [27]), like spatial replication and comparisons of caves showing similar structures to assess patterns of spatio-temporal variability [10], [15], [16]. The adoption of similar approaches, however, implies that the selection of caves to be included in the study is restricted to caves with comparable morphology (e.g. depth, size and general shape), in order to avoid any confounding effect of uncontrolled factors. However, such a ‘forced’ selection of specific (i.e. comparable) types of caves excludes all caves that don’t fit the a priori-selected morphological criteria. Overweighting the need for more experimental rigor in order to get formally perfect data or to reply to specific questions, therefore, carries the risk to lose important pieces of information when the overall diversity of fish is to be captured. Cave structures and related ecological factors, in fact, may indeed greatly change from cave to cave having a variable morphology and other features sometimes difficult to formalize. Such a variability can be mirrored in the structure and diversity of associated fish assemblages (e.g. in terms of species composition and patterns of abundance). Assessing more exhaustive diversity patterns (using an approach that properly takes into consideration natural history issues [28]) can produce useful information, for example when fish assemblages associated with various habitats (including caves) are hosted inside Marine Protected Areas (hereafter MPAs). This is especially true, talking about caves, wherever MPAs are established in karstic regions where marine caves are numerous and variable in structure [5], [29]. So, in some cases, it could be preferable to carry out fish sampling inside marine caves that are structurally as variable as possible. This would maximize the capture of the overall variability and diversity (e.g. in terms of species present) in the associated fish fauna in a given stretch of coast or region.
Along the coasts of Italy (including the main islands of Sicily and Sardinia, and many other small archipelagos), many MPAs have been established in recent years, including in coastal areas rich in marine caves. Although marine caves are listed among the few marine habitats under protection for the European Union (EU Habitat Directive 92/43EEC) and they are becoming more and more popular for recreational diving (a serious threat for many fragile and shy organisms living inside), there are no specific rules or restrictions (except in a few MPAs). In recent years, a number of papers specifically emphasized the contribution of cave assemblages to overall coastal biodiversity (e.g. [[6], [7], [10], [30], [31])and/or assessed the detrimental effects of some human impacts on associated benthic communities (such as unregulated underwater activities; see [32], [33]). This type of information is necessary to implement proper conservation and management measures [34], [35].
The demand for more effective protection and management policies of marine caves in the Mediterranean Sea can be highly supported by evidencing their contribution to marine biodiversity. The information available on the diversity of the fish fauna hosted inside the caves is therefore crucial.
In this study, we thus evaluated 1) the variability in fish species richness and assemblage structure in 14 marine caves of different morphology located inside four Italian MPAs, and 2) the additional contribution of such environments to local fish diversity associated with rocky reefs.
Methods
Ethics statement
All the data collected in the present study have been gathered by using a non destructive methodology (commonly named as ‘Underwater Fish Visual Census’). No fish was collected, injured or manipulated. In addition, scientific divers adopted a proper behavior underwater in order to limit any disturbance into the caves investigated. The research, from a formal point of view, has been funded and committed by the Italian Ministry of the Environment, which is the state authority competent on MPAs in Italy. Funding and commitment implied the authorization to access the MPAs and run the non destructive sampling on fish. In addition, in the occasion of each sampling campaign at each MPA, specific authorizations have been asked and obtained by the management bodies, formally represented by the following MPAs Managers: Gianfranco Russino (Capo Caccia MPA), Salvatore Martello (Lampedusa MPA), Vincenzo Incontro (Plemmirio MPA) and Paolo D’Ambrosio (Porto Cesareo MPA). Permissions from MPAs (besides the one released by the competent Ministry that funded the project) have been obtained in the form of simple letters or emails, so there isn’t any associated authorization numbers or codes.
Study locations
Fish sampling was carried out in September and October 2009 in 14 submerged caves located in 4 Italian MPAs (Fig 1): 1) six caves at Capo Caccia (40° 33′ N, 8° 9′ E), Sardinia between ~5 and 18 m depth; 2) two caves at Lampedusa (35° 29' N—12° 36' E), Pelagie Islands, Sicily between ~10 and 20 m depth; 3) two caves at Porto Cesareo (40° 15' N—17° 53 E), Apulia between 8 and 10 m depth; 4) four caves at Plemmirio (37° 01' N—15° 19' E) near Siracusa, Sicily between ~18 and 30 m depth.
1, Capo Caccia; 2, Lampedusa; 3, Porto Cesareo; 4, Plemmirio.
The investigated caves encompassed both blind caves (one entrance) and caves with several openings, that varied remarkably in terms of morphology, branching and overall extension, presence/absence of an underwater ceiling, depth and characteristics of the bottom (e.g. formed by rocks or muddy sediments, [36], [37]). A detailed description of the investigated marine caves is given in Table 1.
Sampling and data analyses
Fish abundance was estimated using a modified transect visual census method using SCUBA [10]. The scientists-divers who got the fish data within the caves investigated, received a specific training, as it is usually recommended. Marine caves, in fact, typically contain silt on the floor, which can easily be stirred up reducing visibility to zero and making it difficult if not impossible to locate the cave entrance (casualties are unfortunately not that rare). Transects were 8 to 60 m long and 2 m wide, as transect length was adapted to the shape and morphological discontinuities of different cave sectors. Any overlap between transects (which would have implied spatial dependence among replicates and a bias in the statistical analyses, see [27]) has been avoided. We have operatively defined as ‘sub-habitats’ the following sectors identified within the investigated caves: walls (coded as W), ceilings (C), bottoms (B). Four caves (i.e. Falco, Bisbe and Cabirol in the MPA of Capo Caccia and Cave X in the MPA of Porto Cesareo) presented easily accessible ends that were considered as a further sub-habitat type (E). The number of transects performed in each cave was also variable in relation to the extent and topography. Additional sampling was performed on rocky reef habitats outside each cave (codes as O) for comparison. Considering caves and rocky reefs outside the caves, a total of n = 94 visual censuses were performed in the present study (see Table 1 for detail about replication in each cave). With regard to the different sub-habitats, we performed n = 41 transects in W, n = 20 in C, n = 15 in B, n = 4 in E and, in addition, n = 14 in habitat O.
Due to the variable dimensions of transects, abundance values observed in the field were then converted to number of individuals/100 m2. Outside the caves, in agreement with standard methods on rocky reefs [38], visual censuses were carried out along 25 m long and 5 m wide transects. Densities were then converted to 100 m2.
Whole fish assemblage structures (i.e. in terms of species composition and relative abundances) were analyzed using 2-way unbalanced permutational multivariate analysis of variance (PERMANOVA; [39]) according to two factors: ‘caves’ (Ca), random with 14 levels, and ‘sub-habitat’ (SH), fixed with 5 levels (W, C, B, E, and O). Analyses were performed using the PRIMER v6 software [40], implemented with the add-on package permanova+ [41].
PERMANOVA analysis is capable of handling unbalanced multi-factorial experimental designs [41]. In order to avoid any potential bias due to the adoption of transects of different length (as specified above), prior to perform PERMANOVA, we checked for possible correlation among transect length and multivariate data and relevant single variables (i.e. species richness, total density). Specifically we used linear univariate/multivariate regression analyses (DISTLM). Multivariate regression was graphically represented by mean of distance-based redundancy analysis (dbRDA, [42]).
As no evidence of significant relationships was highlighted for all the variables considered (see S1 Fig, S2 Fig and S3 Fig. for supporting results), abundance values/100 m2 were adopted in PERMANOVA analysis.
To visualize multivariate patterns, non-metric multidimensional scaling (nMDS) ordinations were obtained from Bray-Curtis dissimilarity matrices calculated from log(x+1) transformed data. This transformation was selected to balance the contribution to overall abundances of schooling species (like Apogon imberis) and, therefore, reduce the weighting of abundant species and increase that of rarer species.
Results
A total of 59 taxa was recorded in this study (S1 Table). Thirty-eight species were recorded inside the 14 investigated marine caves (Table 2). Twenty-eight, 18, 16 and 15 species were recorded in caves located within Capo Caccia, Porto Cesareo, Plemmirio and Lampedusa MPAs, respectively.
Eighteen species were exclusively found inside the caves (i.e. they were not recorded in the outside rocky reefs) and were represented mainly by speleophilic gobids (e.g. Didogobius splechtnai) and nocturnal predator species (e.g. Conger conger). Forty-one species were censused in the rocky reefs outside, 21 of which were exclusively found outside caves and 20 of which were shared with cave sub-habitats.
Considering cave by cave, the highest number of species (n = 21) was found inside the Nereo cave (the most extended cave among those investigated in this study) at Capo Caccia MPA and the lowest (n = 5) inside the Mazzare cave at Plemmirio MPA (Fig 2). A higher number of species was associated with W sub-habitat (n = 35) compared to B (n = 14), C (n = 12), or E sub-habitat (n = 10).
In terms of frequency of occurrence, Apogon imberbis was the most frequent and widespread fish across the 14 caves investigated (Fig 3), followed by the speleophilic gobid Thorogobius ephippiatus found in 13 caves. Diplodus vulgaris and Scorpaena notata were found in 12 out of 14 caves, followed by Corcyrogobius liechtensteini censused in 11 caves. Other speleophilic gobids, like Gammogobius steinitzi and Didogobius splechtnai, were recorded in 7 and 4 caves, respectively, out of the 14 investigated. Serranus scriba and Chromis chromis have been censused in 9 and 8 caves, respectively. The remaining species were found in 7 or less marine caves out of 14 studied. The speleophilic fish Grammonus ater was quite rare: it was found in 4 out of 14 caves, at Capo Caccia and Plemmirio MPAs. It is worth noting the presence of several specimens of Dasyatis centroura inside the Taccio Vecchio 1 cave at Lampedusa.
PERMANOVA on fish assemblage structures associated with different caves and sub-habitats revealed a significant interaction between the two factors analyzed (Ca x SH; Table 3). Though both the main effects of the two factors investigated (‘caves’ and ‘sub-habitat’) were found to be highly significant, the output about the interaction Ca x HT suggests that there are differences in fish assemblage structures among sub-habitats that, however, are not coherent among caves.
The nMDS plot of samples (i.e. showing all visual census transects; Fig 4) clearly shows that 1) fish assemblages associated with O separate out from those generally associated with caves; 2) fish assemblages associated with W are strongly aggregated (except for one single replicate census where Apogon imberbis, generally very abundant, was absent); 3) fish assemblages associated with C were in some cases similar to those associated with other rocky sub-habitats (e.g., W); 4) assemblages associated with bottoms characterized by a sandy/muddy component separate out from those associated with rocky floors (see Table 1 for details about bottom types in the various caves); 5) fish assemblages recorded in the final cave portions and on the rocky bottom sub-habitats fell within the cloud of points representing the assemblages observed on W.
W: wall; B: bottom (white triangles = presence of sand/mud; dark triangles = ‘pure’ rocky bottoms): C: ceiling; E: end of the cave; O: rocky reefs outside the cave.
Discussion
To the best of our knowledge the number of species reported in this study is the highest ever reported from cave habitats in the Mediterranean Sea. According to Bussotti and Guidetti [10], we found that cryptic and shy species (e.g. Apogon imberbis, Scorpaena notata, Thorogobius ephippiatus, Grammonus ater) were mostly or exclusively found inside the caves. Some of these species were in almost all the caves investigated, with Apogon imberbis being reported everywhere. This result leads us to consider, especially taking into account the large spatial scale explored in this study, that a subset of fish species censused here could actually represent a pool typical of Mediterranean caves.
Other species are reported to be associated with caves, e.g. some Gobiidae such as Odondebuenia balearica, Speleogobius trigloides or Vanneaugobius dollfusi (P. Francour unpublished data; [23] and references therein). In the caves investigated here, the above-mentioned species were not recorded. This study, however, was just based on visual inspection, while destructive investigations using anesthetic [23] could allow to get more exhaustive species lists of cryptic fishes associated with marine caves.
For some speleophilic gobies, we found the same preference for cave sub-habitats as reported by other authors. Corcyrogobius liechtensteini and Gammogobius steinitzi were observed in cave walls and ceilings [13], [14], while Didogobius splechtnai was observed close to the bare rocky walls where this fish uses the small holes as hiding places [13].
In this study, we privileged the inclusion of the environmental variability of submerged marine caves (particularly high at the Capo Caccia MPA) so to maximize gathering information on assemblage diversity. The study, conducted at several locations from which the previous information was quite scarce or even missing, thus allowed to collect interesting and new data on the biogeographic distribution of several species. Some speleophilic gobids have been reported for the first time in some localities where they were not previously reported (Fig 5). To our knowledge Corcyrogobius liechtensteini, for example, was previously reported only in some localities in Croatia [14], [43], Italy (SE Apulia, [16]; Giglio Island, [44]), Spain (Balearic Island [13], [45] and France (near Marseille, [46]; Port-Cros, Scandola, Cap Roux and Nice, P. Francour, unpublished data). In this study, this species has been reported in all MPAs investigated, which confirms the widespread distribution of this fish inside marine caves across the Mediterranean. Gammogobius steinitzi was previously found in Croatia [47], Giglio Island (Italy, [44]), Ibiza island (Spain, [48]), around Marseille and Bagaud Island (France; [46]; [49]), Scandola (Corsica) and Monaco (P. Francour unpublished data). In this study, new records (Capo Caccia and Lampedusa) of G. steinitzi confirm its basin-wide distribution range. Didogobius splechtnai was previously observed in Spain at Ibiza [13] and Cabrera [50], in Italy at Lampedusa [51], Elba and Tavolara islands, in Istria (Croatia; [25]), in various places along the French coast [52], in Corsica (P. Francour unpublished data), and along the southern Aegean Sea coast of Turkey [53]. This study yields new records from Capo Caccia and Porto Cesaro MPAs in Italy.
This study allowed us to census all these gobids, which leads to consider them as common species of cave habitats in the Mediterranean. Patzner [24] stressed that many gobids from the Mediterranean are rarely observed, but also that their rarity is likely to be more apparent than real, due to their small size, economic insignificance and cryptobenthic behavior. In common with many marine taxonomic groups (see [54]), the scarcity of experts capable of identifying small gobies is considered to be another possible reason for interpreting the scarcity of such records [55].
Concerning fish assemblages, this study shows that those associated with marine caves are clearly different from those associated with rocky reefs outside. This evidence is consistent with other more local studies (e.g. [10]). Due to the wider spatial scale of this study, such an evidence can be generalized to a large spatial scale.
The fact that marine caves host different fish assemblages (with some species typical of caves) has never been considered until now in biodiversity/scientific programs aimed, for example, at refining species inventories to maximize fish biodiversity representativity and protection within MPAs in the Mediterranean sea [56], [57]. This shows that until now the contribution of marine caves to local diversity has been substantially neglected. Several fish species that are quite easily detected during daylight hours inside caves (e.g. Conger conger, Phycis phycis, Scorpaena notata) can be hardly detected in rocky reefs outside, because of their nocturnal activity rhythm or because they have a cryptobenthic life style [58], [59]. The cryptobenthic gobid Didogobius splechtnai, for example, that in our study was observed only inside caves, is reported to be closely associated with holes and cavities on coralligenous formations [24], on mud in deep waters [45], on pits covered with gravel [51] and among the rhizomes of Posidonia oceanica beds [25]. In short, therefore, failure to include caves in monitoring will result in an incomplete census of the fish species present.
Another significant finding of this study is that the structural characteristics of marine caves (i.e. variety of cave sub-habitats such as walls, ceilings, bottoms, etc) may significantly affect the species richness and fish assemblage structures inside. Bussotti and Guidetti [10] reported that the structure of fish assemblages changes along the cave axis in tunnel-like caves, from the entrances to the inner portions. Results of this study show that other cave features may be as much important for shaping fish assemblages inside the caves. In accordance with observations made by Bori et al. [60], for example, the complete darkness in the inner cave portions was a condition necessary, but not sufficient to host the strictly speleophilic fish Grammonus ater. This point is reinforced by the observations done in an artificial habitat in Monaco (P. Francour; unpublished data): in the inner parts of totally dark concrete dykes, the main cryptic species were C. liechtensteini, G. steinitzi and G. ater. The nature of the substrate of the cave bottom (e.g. rocky or sandy) also plays an important role in influencing the presence of some species and the assemblage structure: when the nature of the bottom is rocky, then fish assemblages were similar to those associated with the cave walls. A similar response to substrate type and features has been recorded elsewhere, from tropical (e.g. [61]) to temperate systems (e.g. [62]), as well as in the Mediterranean Sea [63].
This study suggests that it is fairly difficult to define a ‘typical’ cave fish assemblage or to quantify the distribution patterns in general terms, as fish assemblages may change significantly from cave to cave. Generalizations concerning distribution patterns of fish assemblages can be made in finer terms by selecting a subset of comparable caves in a certain stretch of coast [10], [15], [16]. A similar approach, however, carries the risk to lose information about those caves that have different characteristics from those chosen a priori for the sake of formal comparisons (i.e. while using complex experimental designs; Underwood, 1997). In Bussotti et al. [15], [16], and Bussotti and Guidetti [10], for example, only blind caves were selected, to specifically aim at testing whether the ‘distance from the entrance’ (and related gradients of light intensity, water motion, etc) was a relevant factor influencing fish distribution inside.
Another important consideration on the results of this study concerns the biodiversity and the related possible conservation measures to implement. It is worth noting the presence in some caves of fish species included in the Red List IUCN [64], such as the dusky grouper Epinephelus marginatus and the thorny stingray Dasyatis centroura (present exclusively in the Lampedusa MPA), or in the annex III of the Barcelona Convention, such as the brown meagre Sciaena umbra. Their presence and frequency within cave habitats can be a valuable tool to support the inclusion of these environments inside MPAs. Some Gobiidae species closely related to marine caves (such as C. liechtensteini, D. splechtnai, G. steinitzi, O. balearica, S. trigloides), on the contrary, are generally indicated as DD (‘data deficient’) species in the last assessment of the Red List for the Mediterranean fish. Their association with marine caves, therefore, should be considered in future conservation plans in terms of their contribution to local diversity.
In conclusion, this study allowed to improve and refine the available knowledge on fish diversity in submerged caves in the Mediterranean context. In particular, due to the overall diversity they support, the presence of valuable species for conservation and the ecological role they may fulfill (all this showed in the present and previous studies), submerged marine caves should be prioritized for inclusion within future MPAs and into larger scale marine spatial management plans through the Mediterranean Sea.
Supporting Information
S1 Dataset. Densities of fish detected from each cave and outside rocky reefs.
https://doi.org/10.1371/journal.pone.0122632.s001
(XLS)
S1 Fig. Distance based redundancy analysis (DbRDA) plot of multivariate data constrained to transect length.
https://doi.org/10.1371/journal.pone.0122632.s002
(DOCX)
S2 Fig. Total fish density of each sample (i.e. transect) against transect length.
https://doi.org/10.1371/journal.pone.0122632.s003
(DOCX)
S3 Fig. Species richness of each sample (i.e. transect) against transect length.
https://doi.org/10.1371/journal.pone.0122632.s004
(DOCX)
S1 Table. Fish species recorded at the four cave sub-habitats and outside rocky reefs investigated in this study.
https://doi.org/10.1371/journal.pone.0122632.s005
(DOC)
Acknowledgments
We would like to thank Dr Fabio Bulleri (University of Pisa, Italy) for his advice concerning statistical analysis, Ernesto Azzurro (ISPRA, Italy) for his elucidations on lessepsian fishes and two anonymous reviewers for greatly improving the manuscript. The manuscript is dedicated to the memory of Gaetano Ferruzza and Dario Romano (who dramatically died while diving and working inside one of the caves investigated here) and Fabio Cicogna (who passed away some years ago and who consecrated his last years in promoting research and improving knowledge on Mediterranean marine caves).
Author Contributions
Conceived and designed the experiments: SB PG. Performed the experiments: SB PG. Analyzed the data: SB ADF PF PG. Contributed reagents/materials/analysis tools: SB ADF PF PG. Wrote the paper: SB ADF PF PG.
References
- 1.
Cicogna F, Bianchi CN, Ferrari G, Forti P (2003) Grotte marine: cinquant’anni di ricerca in Italia. CLEM, Ministero dell’Ambiente e della tutela del Territorio, Rapallo, 505 pp.
- 2.
Riedl R (1966) Biologie der Meereshohlen. Paul Parey, Hamburg and Berlin, 636 pp.
- 3. Bianchi CN, Cattaneo-Vietti R, Cinelli F, Morri C, Pansini M (1996) Lo studio biologico delle grotte sottomarine del Mediterraneo: conoscenze attuali e prospettive. Boll Mus Ist Biol Univ Genova 60–61: 41–69.
- 4. Harmelin JG, Vacelet J, Vasseur P (1985) Les grottes sous-marines obscures: un milieu extrême et un remarquable biotope refuge. Téthys 11 (3–4): 214–229.
- 5. Bussotti S, Terlizzi A, Fraschetti S, Belmonte G, Boero F (2006) Spatial and temporal variability of sessile benthos in shallow Mediterranean marine caves. Mar Ecol Prog Ser 325: 109–119.
- 6. Parravicini V, Guidetti P, Morri C, Montefalcone M, Donato M, Bianchi CN (2010) Consequences of sea water temperature anomalies on a Mediterranean submarine cave ecosystem. Estuar Coast Shelf S 86: 276–282.
- 7. Gerovasileiou V, Voultsiadou E (2012) Marine caves of the Mediterranean Sea: a sponge biodiversity reservoir within a biodiversity hotspot. PLoS ONE 7(7): e39873. pmid:22808070
- 8. Connell JH (1961) The influence of interspecific competition and other factors on the distribution of the barnacle Chthamalus stellatus. Ecology 42: 315–328.
- 9. Jackson JBC (1977) Competition on marine hard substrata: the adaptive significance of solitary and colonial strategies. Am Nat 111: 743–767.
- 10. Bussotti S, Guidetti P (2009) Do Mediterranean fish assemblages associated with marine caves and rocky reefs differ? Estuar Coast Shelf S 81: 65–73.
- 11. Abel EF (1959) Zur Kenntnis der Beziehungen der Fische zu Ho hlen im Mittelmeer. Pubbl Staz Zool Napoli 30: 519–528.
- 12. Kotrschal K (1983) Northern Adriatic rocky reef fishes at low winter temperatures. PSZN Mar Ecol 4: 275–286.
- 13. Herler J, Patzner RA, Ahnelt H, Hilgers H (1999) Habitat selection and ecology of two speleophilic gobiid fishes (Pisces: Gobidae) from the Western Mediterranean Sea. PSZN Mar Ecol 20: 49–62.
- 14. Arko-Pijevac M, Benac C, Kovacic M, Kirincic M (2001) A submarine cave at the Island of Krk (North Adriatic Sea). Nat Croat 10: 163–184.
- 15. Bussotti S, Denitto F, Guidetti P, Belmonte G (2002) Fish assemblages in shallow marine caves of the Salento Peninsula (Southern-Apulia, SE Italy). PSZN Mar Ecol 23: 11–20.
- 16. Bussotti S, Guidetti P, Belmonte G (2003) Distribution patterns of the cardinal fish, Apogon imberbis, in shallow marine caves in southern Apulia (SE Italy). Ital J Zool 70: 153–157.
- 17. Oertel A, Patzner RA (2007) The biology and ecology of a submarine cave: the Grotta del Bel Torrente (Central-East Sardegna, Italy). Mar Ecol 28: 60–65.
- 18.
Azzurro E, Goren M, Diamant A, Galil B, Bernardi G (2014) Establishing the identity and assessing the dynamics of invasion in the Mediterranean Sea by the dusky sweeper, Pempheris rhomboidea Kossman & Räuber, 1877 (Pampheridae, Perciformes). Biol Inv https://doi.org/10.1007/s10530-014-0836-5
- 19. Bilecenoglu M, Taskavak E (1999) Some observations on the habitat of the Red Sea immigrant sweeper, Pempheris vanicolensis, on the Mediterranean coast of Turkey. Zool Middle East 17: 67–70.
- 20.
Muths D, Rastorgueff PA, Selva M, Chevaldonné P (2014) Local scale connectivity in the cave-dwelling brooding fish Apogon imberbis. J Sea Res. https://doi.org/10.1016/j.seares.2014.10.009
- 21.
Otero M, Cebrian E, Francour P, Galil B, Savini D (2013) Monitoring marine invasive species in Mediterranean marine protected areas (MPAs): A strategy and practical guide for managers. IUCN, Malaga, 136 pp.
- 22. Zander CD (1990) Benthic fishes of sea caves as components of the mesolithion in the Mediterranean Sea. Mem Biospéol 17: 17–54.
- 23. Kovačić M (1997) Cryptobenthic gobies and clingfishes in the Kvarner area, Adriatic Sea. Nat Croat 6: 423–435.
- 24. Patzner RA (1999) Habitat utilization and depth distribution of small cryptobenthic fishes (Blenniidae, Gobiesocidae, Gobiidae, Tripterygiidae) in Ibiza (western Mediterranean Sea). Environ Biol Fishes 55: 207–214.
- 25. Herler J, Patzner RA (2002) New records of Didogobius splechtnai (Gobiidae) from the Tyrrhenian and Northern Adriatic sea. Cybium 26: 153–155.
- 26. Gerovasileiou V, Trygonis V, Sini M, Koutsoubas D, Voultsiadou E (2013) Three-dimensional mapping of the marine caves using a handheld echosounder. Mar Ecol Prog Ser 486:13–22.
- 27.
Underwood AJ (1997) Experiments in Ecology: their logical design and interpretation using analysis of variance. University Press, Cambridge, pp. 524.
- 28. Guidetti P, Parravicini V, Morri C, Bianchi CN (2014) Against nature? Why ecologists should not diverge from natural history. Vie et Milieu 64: 1–8.
- 29. Suric M, Loncaric R, Loncar N (2010) Submerged caves of Croatia: distribution, classification and origin. Environ Earth Sci 61: 1473–1480.
- 30. Todaro MA, Leasi F, Bizzarri N, Tongiorgi P (2006) Meiofauna densities and gastrotrich community composition in a Mediterranean sea cave. Mar Biol 49: 1079–1091.
- 31.
Gerovasileiou V, Voultsiadou E (2014) Mediterranean marine caves as biodiversity reservoirs: a preliminary overview. In: Langar H, Bouafif C, Ourghi A, editors. Proceedings of the first Mediterranean Symposium on the conservation of dark habitats, RAC/SPA; 2014. pp. 45–50.
- 32. Di Franco A, Ferruzza G, Baiata P, Chemello R, Milazzo M (2010) Can recreational scuba divers alter natural gross sedimentation rate? A case study from a Mediterranean deep cave. Ices J Mar Sci 67: 871–874.
- 33. Guarnieri G, Terlizzi A, Bevilacqua S, Fraschetti S (2012) Increasing heterogeneity of sensitive assemblages as a consequence of human impact in submarine caves. Mar Biol 159: 1155–1164.
- 34.
Abdulla A, Gomei M, Maison E, Piante C (2008) Status of Marine Protected Areas in the Mediterranean Sea. France: IUCN, Malaga, and WWF France, 152 pp.
- 35.
Giakoumi S, Sini M, Gerovasileiou V, Mazor T, Beher J, Possingham HP, et al. (2013) Ecoregion-based conservation planning in the Mediterranean: dealing with large-scale heterogeneity. PLoS ONE: https://doi.org/10.1371/journal.pone.0076449
- 36. Leonardi R (1994) Contributo alla conoscenza delle grotte sommerse della Penisola della Maddalena (SR). Boll Acc Gioenia Sci Nat 27: 599–620.
- 37. Ferrari G (2005) Grotte marine a Lampedusa. Thal Sal 29 (suppl): 117–138.
- 38. Harmelin-Vivien ML, Harmelin JG, Chauvet C, Duval C, Galzin R, Lejeune P, et al. (1985) Evaluation des peuplements et populations de poissons. Méthodes et problèmes. Rev Ecol (Terre Vie) 40: 467–539.
- 39. Anderson MJ (2001) A new method for non-parametric multivariate analysis of variance. Austral Ecol 26: 32–46. pmid:11469182
- 40.
Clarke KR, Gorley, RN (2006) primer V6: user manual/tutorial. PRIMER-E Ltd, Plymouth, UK, 192pp.
- 41.
Anderson MJ, Gorley RN, Clarke KR (2008) PERMANOVA+ for PRIMER: Guide to Software and Statistical Methods PRIMER-E, Plymouth, UK, 214 pp.
- 42. McArdle BH, Anderson MJ (2001) Fitting multivariate models to community data: a comment on distance-based redundancy analysis. Ecology 82: 290–297.
- 43. Ahnelt H, Miller PJ, Patzner RA (1994) Systematics and distribution of two rare Mediterranean gobies, Corcyrogobius liechtensteini and Odondebuenia balearica (Teleostei: Gobiidae). Cybium 18: 169–176.
- 44. Ahnelt H, Herler J, Scsepka S, Patzner RA (1998) First records of two rare Mediterranean Gobiidae in the northern Tyrrhenian Sea. Cybium 22: 183–186.
- 45. Ahnelt H, Dorda J (2004) Gobioid fishes from the north eastern Atlantic and the Mediterranean: new records and rarely found species. Ann Naturhist Mus Wien 105: 5–19.
- 46. Scsepka S, Ahnelt H (1999) Wiederbeschreibung von Gammogobius steinitzi Bath 1971 sowie ein Erstnachweis von Corcyrogobius liechtensteini (Kolombatovic 1891) für Frankreich. Senck biol 79: 71–81.
- 47. Kovačić M (1999) Gammogobius steinitzi Bath, 1971, a fish new to the Adriatic Sea. Nat Croat 6: 1–7.
- 48. Ahnelt H, Patzner RA (1996) Kryptobenthische Meergrundeln von den Balearen (Westliches Mittelmeer) mit Anmerkungen zum Unterartstatus von Chromogobius zebratus levanticus. Ann Nat Hist Mus Wien 98B: 529–544.
- 49. Harmelin JG, Boury-Esnault N, Fichez R, Vacelet J, Zibrowius H (2003) Peuplement de la grotte sous-marine l’île de Bagaud (parc national de Port-Cros, France, Méditerranée). Sci Rep Port-Cros nation Park, Fr. 19: 117–134.
- 50.
Ballesteros E (2007) Los fondos marinos del Archipielago de Cabrera. In: Araujo J, Moreno J, Ramis JA, Castro EB, Ballesteros E, Sampedro JL, Savater F, Fuente OR (eds) El parque nacional del Archipilago de Cabrera. Ministerio de Defensa, Secretaria General Tecnica. pp 140–171.
- 51. Stefanni S (1999) A new record of Didogobius splechtnai Ahnelt & Patzner, 1995 (Gobiidae) from the central Mediterranean Sea. Cybium 23: 105–107.
- 52. Francour P (2008) First records of Didogobius splechtnai along the French Mediterranean coast and additional comments about D. schlieweni. Acta Ichthyol Piscat 38: 139–141.
- 53. Francour P, Bilecenoglu M, Kaya M (2007) In situ observation on new and rare gobies from the Eastern Mediterranean sea. Rapp Comm int Mer Médit 38: 478.
- 54. Giangrande A, Licciano M (2004) Factors influencing latitudinal pattern of biodiversity: an example using Sabellidae (Anellida, Polichaeta). Biodivers Conserv 13: 1633–1646.
- 55. Guidetti P, Bussotti S, Kovacic M (2006) First record of the large-scaled goby, Thorogobius macrolepis (Pisces, Gobiidae), in Italian seas. Thal Sal 29: 41–45.
- 56. Guidetti P, Milazzo M, Bussotti S, Molinari A, Murenu M, Pais A, et al. (2008) Italian marine reserve effectiveness: does enforcement matter? Biol Conserv 141: 699–709.
- 57. La Mesa G, Guidetti P, Bussotti S, Cattaneo-Vietti R, Manganaro A, Molinari A, et al. (2013) Rocky reef fish assemblages at six Mediterranean marine protected areas: broad-scale patterns in assemblage structure, species richness and composition. Ital J Zool 80: 90–103.
- 58. Willis TJ (2001) Visual census methods underestimate density and diversity of cryptic reef fishes. J Fish Biol 59: 1408–1411.
- 59. Azzurro E, Pais A, Consoli P, Andaloro F (2007) Evaluating day night changes in shallow Mediterranean rocky reef fish assemblages by visual census. Mar Biol 151: 2245–2253.
- 60. Bori C, Gili JM, Garcìa A (1985) Presencia de Oligopus ater Risso, 1810 (Pisces, Ophidiiformes) en cuevas submarinas del litoral NE de Mallorca. Misc Zool 9: 401–404.
- 61. Luckhurst BE, Luckhurst K (1978) Analysis of the influence of substrate variables on coral reef fish munities. Mar Biol 49: 317–323.
- 62. Connell SD, Jones GP (1991) The influence of habitat complexity on post-recruitment processes in a temperate reef fish population. J Exp Mar Biol Ecol 151: 271–294.
- 63. Guidetti P (2000) Differences among fish assemblages associated with nearshore Posidonia oceanica seagrass beds, rocky–algal reefs and unvegetated sand habitats in the Adriatic Sea. Estuar Coast Shelf S 50: 515–529.
- 64.
Abdul Malak D, Livingstone SR, Pollard D, Polidoro BA, Cuttelod A, Bariche M et al. (2011) Overview of the Conservation Status of the Marine Fishes of the Mediterranean Sea. Gland, Switzerland and Malaga, Spain: IUCN, 72 pp.