Next Article in Journal
Preliminary Insights on the Habitat Use and Vertical Movements of the Pelagic Stingray (Pteroplatytrygon violacea) in the Western Mediterranean Sea
Next Article in Special Issue
Population Dynamics Parameters and Exploitation Status of 55 Commercial Species in Egyptian Red Sea Fisheries: A Key to Sustainable Fisheries
Previous Article in Journal
Transcriptional Analysis Reveals the Iron Regulation Network of the Pathogenic Yeast Metschnikowia bicuspidata in Response to Iron Stress
Previous Article in Special Issue
Application of the Method Evaluation and Risk Assessment Tool for a Small-Scale Grouper Fishery in Indonesia
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Fishes
Volume 9
Issue 6
10.3390/fishes9060237
fishes-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Communication

First Record of the Red Cornetfish Fistularia petimba Lacepède, 1803 from Amorgos Island (Central Aegean Sea; Greece) and a Review of Its Current Distribution in the Mediterranean Sea

by
Nefeli Tsaousi
and
Stefanos Kalogirou
*
Laboratory of Applied Hydrobiology, Department of Animal Science, School of Animal Sciences, Agricultural University of Athens, Iera Odos 75, 11855 Athens, Greece
*
Author to whom correspondence should be addressed.
Fishes 2024, 9(6), 237; https://doi.org/10.3390/fishes9060237
Submission received: 25 April 2024 / Revised: 14 June 2024 / Accepted: 17 June 2024 / Published: 18 June 2024
(This article belongs to the Special Issue Diagnosis and Management of Small-Scale and Data-Limited Fisheries)
Browse Figures
Review Reports Versions Notes

Abstract

:
The rapid spread of non-native species (NNS) poses a significant threat to biodiversity globally, with the Mediterranean region being particularly susceptible due to increased human activities and its status as a marine biodiversity hotspot. In this study, we focus on the introduction and distribution of Fistularia petimba, a member of the Fistulariidae family, in the eastern Mediterranean Sea and a record from the coasts of Amorgos Island, Greece. Through a baseline fishery study conducted over 12 months, utilizing experimental sampling with gillnets, trammel nets, and longlines, one individual of F. petimba was captured off the coast of Katapola Bay. Morphological examination confirmed its identity, with measurements on meristic characteristics obtained and the stomach content analysed. This finding represents a significant addition to the documented distribution of F. petimba in the Mediterranean Sea, particularly in the Aegean Sea, underscoring the importance of ongoing research in uncovering new occurrences and expanding our understanding of marine biodiversity and ecosystem changes. Further investigation into the ecological preferences and population dynamics of F. petimba in the Aegean Sea is crucial for informed conservation and management efforts if this species is considered to be established.
Keywords:
Fistularia petimba; red cornetfish; Mediterranean Sea; invasive species; non-native species; Lessepsian species; marine biodiversity; species distribution
Key Contribution: This study provides a review of a recent non-native species geographical distribution. This study provides insights on the crucial establishment phase for the species and signifies areas for further investigation to reveal life trait characteristics and succession rate.

1. Introduction

One of the main threats that biodiversity currently faces is the rapid spread of non-native species (NNS). NNS are defined as an array of species spreading outside their natural or native distribution range [1]. Different areas worldwide have been experiencing vast impacts from the introduction of NNS, often related to increased human activities, such as the opening of canals, the continuous growth of the shipping industry across biogeographic barriers [2,3], a wide range of changes in water temperature due to climate change [4,5,6], fishing pressure [7,8,9], and habitat degradation or loss of species [10,11,12]. In the studied area of the Mediterranean Sea, recognized as one of the main hotspots of marine biodiversity [13,14], the effects of NNS are apparent, both in terms of introduction rate [15] and number of introduced species [16], leading to the global acknowledgment of the Mediterranean region as a hotspot area for NNS [17].
A region where visible changes in aquatic biodiversity have occurred is the eastern Mediterranean Sea, where a rapid introduction of fish species of Indo-Pacific origin are observed, i.e., the Levantine Sea [18,19,20,21], significantly raising the overall amount of fish biomass up to 90% in specific habitats [22,23]. These habitats include hard bottoms for Siganus luridus and Siganus rivulatus, and sandy bottoms and seagrass meadows for the Lagocephalus sceleratus [22]. Though Indo-Pacific fish species could potentially arrive through various ways in the Levantine Basin, they most likely arrive through immigration via the Suez Canal, which opened to shorten the commercial shipping ways between the Indian Ocean and the Mediterranean Sea in 1869 [24]. It is assumed that species that normally resided in the Red Sea and the Indian Ocean traversed through the Suez Canal and proceeded northwards along the Levant coast, actively or passively aided by human activity [25]. These species were named Lessepsian after the name of the constructor of the canal, engineer, and diplomat Ferdinand de Lesseps [26].
The aforementioned group of Lessepsian species established in the Mediterranean Sea currently includes Fistularia commersonii [27] and Fistularia petimba, also called cornetfishes or flutemouths, which belong to the Fistulariidae (order of Syngnathiformes). There is only one genus in this family, Fistularia, and four different species: Fistularia commersonii Rüppell, 1838; Fistularia corneta Gilbert and Starks, 1904; Fistularia petimba Lacepède, 1803; and Fistularia tabacaria Linnaeus, 1758 [28]. The species F. tabacaria inhabits the tropical Atlantic, while its closest relative F. commersonii inhabits the Pacific and Indian Oceans. Fistularia petimba spans the tropical Atlantic and Indo-West Pacific Oceans, whereas F. corneta is confined to the tropical eastern Pacific [29]. Fistularidae species are predators, inhabiting shallow waters of tropical and subtropical areas [29]. Although F. commersonii originated from the Indo-Pacific region [30], a wide geographical distribution has been observed in the eastern Mediterranean Sea [31], with multiple sightings of this Lessepsian immigrant. Due to its rapid growth and reproduction cycle, it has successfully formed large populations in the areas where it has been established, with notable ecological impacts on the native species [32]. Fistularia commersonii is a piscivorous species, mainly feeding on smaller fish and complementing its diet with some Crustacea species. As the size of the species increases, a corresponding increase in the size of prey consumed has been found [32].
The studied red cornetfish, F. petimba, is native to the Indo-West Pacific, the tropical Atlantic [30], and the East Atlantic Ocean [33]. With a time lag of 20 years since its first siting in the western Mediterranean Sea (1996), it has been reported in several locations in the eastern Mediterranean Sea over the last ten years [34,35]. In this study, we show the immigration path of F. petimba in the eastern Mediterranean Sea through a stepping stone process of establishment through the Suez Canal [36,37].

2. Materials and Methods

2.1. Sampling Methodology

A monthly experimental fishery sampling was performed in Amorgos Island, Central Aegean Sea, between September 2022 and August 2023 (Figure 1).
The sampling method used involved three types of gears: gillnets (GNSs), trammel nets (GTRs), and long lines (LLSs). The gears used were designed to study the population dynamics of targeted fisheries species.
For GNSs and GTRs, nine different mesh sizes (20, 22, 24, 26, 28, 30, 32, 36, 45 in mm) were used, and for LLS six different hook sizes (9, 10, 11, 12, 13, 14) were used to reflect the most commonly used mesh and hook sizes in small-scale fisheries of the Aegean Sea.
The nets used in this study had a total length of 900 m, consisting of 100-m panels for each of the nine mesh sizes. The height of each compartment was 100 meshes. The arrangement of mesh sizes for both GNSs and GTRs were randomly selected and are illustrated in Figure 2 and Figure 3. For longlines, each compartment had a length of 200 m and was equipped with 200 hooks (100 hooks per hook size). One compartment comprised of hook sizes 9 and 10, and two more compartments comprised of combinations of hook sizes 11–12 and 13–14, respectively.
All species samples were stored in a freezer (−20 °C) until transportation and were deposited to the Laboratory of Applied Hydrobiology of the Agricultural University of Athens, Greece, for further examination.

2.2. Identification of the Species

Fistularia petimba was identified based on its morphological characteristics [29], following the genus description given by Fritzsche (1976): Fistularia species can be identified by their elongated body.
Fistularia petimba was distinguished from its confamilial species by its specific morphological features [29]: number of rays on the dorsal fin (13–17) and the anal fin (13–16), elongated bony plates embedded in the skin along the midline of the back, with posterior lateral line ossifications terminating in a retrorse spine (Figure 4).
The morphometric characteristics shown in Table 1 were measured to the nearest second decimal in mm.

2.3. Distibution of F. petimba in the Mediterranean Sea

To compile a map with records of F. petimba in the Mediterranean Sea, a literature review (until February 2024) was performed using Google Scholar. This review used two main keywords, namely “Fistularia petimba” and “Red cornetfish”, together with additional keywords to assure that F. petimba records were not missed: “Mediterranean Sea”, “Invasive species”, “NNS”, “ecology”, “habitat”, and “lessepsian”.
To visualize the species’ geographical distribution in the Mediterranean Sea, a map illustrating the occurrences of F. petimba was generated using ArcGIS [38] and by integrating data from this study and published records from scientific journals.

3. Results

An individual of F. petimba (Figure 4) was captured using trammel nets (GTRs) with a mesh size of 26 mm, deployed between 24.5 m and 30.6 m depth on the 27th of May 2023 at 7:50 p.m. and hauled on the 28th of May 2023 at 6:40 a.m. (soak time 11 h and 50 min) off the coast of Katapola Bay, Amorgos Island, Greece (lon = “25.85879922” lat = “36.82760281”). The specimen had a total length of 395.00 mm and a total wet weight of 34 g. The measurements for each of the morphometric characteristics of the species are presented in Table 1.

4. Discussion

The increases in global trade and travel have also increased the chances for species to migrate, immigrate, or establish in areas beyond their native ranges, i.e., through widening and deepening canals or ballast water transport [39,40]. Immigration is most commonly associated with human intervention, such as the opening of canals. The Suez Canal, since its completion in the late 19th century, has served as a major conduit for the immigration of marine organisms between the Red Sea (and Indian Ocean) and the Mediterranean Sea. This artificial connection has facilitated the establishment of numerous NNS in the Mediterranean Basin, reshaping the region’s biodiversity and ecological dynamics [41,42]. When an area is invaded, it becomes a source for the subsequent spread of the organism to other locations in the basin [41]. Marinas in the Mediterranean Sea have been identified as significant areas for the establishment of NNS, not only for initial introductions, but also for subsequent secondary invasions, acting as stepping stones in the spread of NNS [40,43].
In the marine environment, NNS can become invasive, resulting in the displacement of native species, thus leading to a range of negative consequences. These effects encompass the loss of native genetic diversity, alterations to habitats, shifts in community composition, changes to food web dynamics and ecosystem functions, disruptions to the provision of ecosystem services, threats to human health, and significant economic damages [44].
The capture of Fistularia petimba in Amorgos Island (Central Aegean Sea) represents a significant addition to the existing knowledge of the species’ distribution in the Mediterranean region. Prior to this finding, 31 sightings were reported from the Mediterranean Sea, out of which only 1 was in the Aegean Sea, specifically in Samos Island (Figure 5, Table 2). The first record in Cadiz, Spain, appears to be an incidental catch from the Atlantic Ocean, while the subsequent occurrences, mainly in the eastern Mediterranean Sea, reveal a progressive invasion pattern from the Indo-Pacific region and the Red Sea into novel habitats. The review of its current distribution reveals its dispersal path along the coasts of Syria, Egypt, and Turkey. The species’ course is validated with further records from Cyprus and its possible establishment within the Aegean Sea. Due to the lack of available data on the potential impact of F. petimba on native species in the Mediterranean Sea, insights can be drawn from its closely related species, Fistularia commersonii. Fistularia commersonii is mainly piscivorous but also feeds on crustaceans [32]. It has a high reproductive rate and a prolonged spawning season extending from May to August, allowing for rapid population growth [45]. More than 70% of Fistularia commersonii’s diet includes economically valuable species. Its predation on small fish near the seabed, where they hatch and grow, disrupts ecosystem balance and reduces fish biomass [32]. This species quickly establishes itself in new environments, leading to significant ecological and economic consequences, including damage to fisheries (although gradually introduced to consumers) [32,45]. Given the similarities between F. petimba and F. commersonii, it is likely that F. petimba could have similar effects on the Mediterranean ecosystem. Effective monitoring and management strategies are crucial to mitigate these potential impacts. Each documented occurrence represents a critical point in the species’ biogeographic spread throughout the eastern Mediterranean Sea. This review of chronological records offers valuable insights into the stepping stone spread of F. petimba establishment in the Mediterranean Sea. Tracking its cross-border path from the Red Sea to the eastern Mediterranean Sea with subsequent records in the Aegean Sea provides valuable insights into the species’ establishment phase. As reproduction is a crucial part of the successful establishment of species in new areas, Papageorgiou et al. 2023 [46] estimated that the mean total length for gonad maturity was 440 mm for females and 410 mm for males. The results of Papageorgiou et al. 2023 [46] are in accordance with our results, wherein no visible gonads could be identified macroscopically.

5. Conclusions

The occurrence of F. petimba in Amorgos Island suggests a wider presence within the Aegean Sea than previously recognized. This finding underscores the importance of ongoing fishery research and marine monitoring in uncovering new occurrences and expanding our understanding of marine biodiversity in the region. Further investigations into the ecological preferences, population dynamics, life traits, and potential impacts of Fistularia petimba in the Aegean Sea and the Mediterranean Basin are important to understand succession rates and ecological impacts, to enhance conservation efforts, and to inform sustainable management practices.

Author Contributions

Conceptualization, S.K.; Methodology, S.K.; Validation, S.K.; Formal analysis, N.T. and S.K.; Investigation, N.T. and S.K.; Data curation, N.T. and S.K.; Writing—original draft, N.T. and S.K.; Writing—review & editing, N.T. and S.K.; Project administration, S.K.; Funding acquisition, S.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research was co-funded by Blue Marine Foundation (BMF) and Cyclades Preservation Fund (CPF)—Conservation Collective (CC) under the project entitled “Base line study for fisheries management on coastal areas based on local ecological knowledge in Amorgos Island”.

Institutional Review Board Statement

Not applicable for projects funded prior to 2022 (Greek Official Government Gazette Law 4957 FEK A 141/21.07.2022). The project under which data were collected for this study were granted in June 2022; only projects with a starting date after 21 July 2022 are subject to ethical review.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data is contained within the article.

Acknowledgments

The authors thank the Professional Fishing Association of Amorgos and Ioannis Vekris for their expertise and assistance throughout all aspects of our study.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. European Environment Agency. Climate Change, Impacts and Vulnerability in Europe EEA. 2012. Available online: https://www.eea.europa.eu/publications/climate-impacts-and-vulnerability-2012 (accessed on 25 February 2024).
  2. Lewis, S.L.; Maslin, M.A. Defining the Anthropocene. Nature 2015, 519, 171–180. [Google Scholar] [CrossRef] [PubMed]
  3. Pyšek, P.; Hulme, P.E.; Simberloff, D.; Bacher, S.; Blackburn, T.M.; Carlton, J.T.; Dawson, W.; Essl, F.; Foxcroft, L.C.; Genovesi, P.; et al. Scientists’ warning on invasive alien species. Biol. Rev. Camb. Philos. Soc. 2020, 95, 1511–1534. [Google Scholar] [CrossRef] [PubMed]
  4. Genner, M.J.; Sims, D.W.; Wearmouth, V.J.; Southall, E.J.; Southward, A.J.; Henderson, P.A.; Hawkins, S.J. Regional climatic warming drives long-term community changes of British marine fish. Proc. Biol. Sci. 2004, 271, 655–661. [Google Scholar] [CrossRef] [PubMed]
  5. Munday, P.L.; Jones, G.P.; Pratchett, M.S.; Williams, A.J. Climate change and the future for coral reef fishes. Fish Fish. 2008, 9, 261–285. [Google Scholar] [CrossRef]
  6. Simpson, S.D.; Jennings, S.; Johnson, M.P.; Blanchard, J.L.; Schön, P.-J.; Sims, D.W.; Genner, M.J. Continental Shelf-Wide Response of a Fish Assemblage to Rapid Warming of the Sea. Curr. Biol. 2011, 21, 1565–1570. [Google Scholar] [CrossRef] [PubMed]
  7. Pauly, D.; Christensen, V.; Dalsgaard, J.; Froese, R.; Torres, F. Fishing Down Marine Food Webs. Science 1998, 279, 860–863. [Google Scholar] [CrossRef] [PubMed]
  8. Jennings, S.; Alvsvåg, J.; Cotter, A.J.R.; Ehrich, S.; Greenstreet, S.P.R.; Jarre-Teichmann, A.; Mergardt, N.; Rijnsdorp, A.D.; Smedstad, O. Fishing effects in northeast Atlantic shelf seas: Patterns in fishing effort, diversity and community structure. III. International trawling effort in the North Sea: An analysis of spatial and temporal trends. Fish. Res. 1999, 40, 125–134. [Google Scholar] [CrossRef]
  9. Daan, N.; Gislason, H.; Pope, J.G.; Rice, J.C. Changes in the North Sea fish community: Evidence of indirect effects of fishing? ICES J. Mar. Sci. 2005, 62, 177–188. [Google Scholar] [CrossRef]
  10. Jones, G.P.; McCormick, M.I.; Srinivasan, M.; Eagle, J.V. Coral decline threatens fish biodiversity in marine reserves. Proc. Natl. Acad. Sci. USA 2004, 101, 8251–8253. [Google Scholar] [CrossRef]
  11. Airoldi, L.; Balata, D.; Beck, M.W. The Gray Zone: Relationships between habitat loss and marine diversity and their applications in conservation. J. Exp. Mar. Biol. Ecol. 2008, 366, 8–15. [Google Scholar] [CrossRef]
  12. Wilson, S.K.; Fisher, R.; Pratchett, M.S.; Graham, N.A.J.; Dulvy, N.K.; Turner, R.A.; Cakacaka, A.; Polunin, N.V.C.; Rushton, S.P. Exploitation and habitat degradation as agents of change within coral reef fish communities. Glob. Chang. Biol. 2008, 14, 2796–2809. [Google Scholar] [CrossRef]
  13. Myers, N.; Mittermeier, R.A.; Mittermeier, C.G.; da Fonseca, G.A.B.; Kent, J. Biodiversity hotspots for conservation priorities. Nature 2000, 403, 853–858. [Google Scholar] [CrossRef] [PubMed]
  14. Coll, M.; Piroddi, C.; Steenbeek, J.; Kaschner, K.; Ben Rais Lasram, F.; Aguzzi, J.; Ballesteros, E.; Bianchi, C.N.; Corbera, J.; Dailianis, T.; et al. The biodiversity of the Mediterranean Sea: Estimates, patterns, and threats. PLoS ONE 2010, 5, e11842. [Google Scholar] [CrossRef]
  15. Zenetos, A.; Gofas, S.; Verlaque, M.; Cinar, M.E.; Garcia Raso, J.E.; Bianchi, C.N.; Morri, C.; Azzurro, E.; Bilecenoglu, M.; Froglia, C.; et al. Alien species in the Mediterranean Sea by 2010. A contribution to the application of European Union’s Marine Strategy Framework Directive (MSFD). Part I. Spatial distribution. Mediterr. Mar. Sci. 2010, 11, 381. [Google Scholar] [CrossRef]
  16. Costello, M.J.; Coll, M.; Danovaro, R.; Halpin, P.; Ojaveer, H.; Miloslavich, P. A Census of Marine Biodiversity Knowledge, Resources, and Future Challenges. PLoS ONE 2010, 5, e12110. [Google Scholar] [CrossRef] [PubMed]
  17. Ambrogi, A.O. Biotic Invasions in a Mediterranean Lagoon. Biol. Invasions 2000, 2, 165–176. [Google Scholar] [CrossRef]
  18. Goren, M.; Galil, B.S. A review of changes in the fish assemblages of Levantine inland and marine ecosystems following the introduction of non-native fishes. J. Appl. Ichthyol. 2005, 21, 364–370. [Google Scholar] [CrossRef]
  19. Harmelin, M.; Bitar, G.; Harmelin, J.-G.; Monestiez, P. The littoral fish community of the Lebanese rocky coast (eastern Mediterranean Sea) with emphasis on Red Sea immigrants. Biol. Invasions 2005, 7, 625–637. [Google Scholar] [CrossRef]
  20. Parravicini, V.; Azzurro, E.; Kulbicki, M.; Belmaker, J. Niche shift can impair the ability to predict invasion risk in the marine realm: An illustration using Mediterranean fish invaders. Ecol. Lett. 2015, 18, 246–253. [Google Scholar] [CrossRef]
  21. Raitsos, D.; Beaugrand, G.; Georgopoulos, D.; Zenetos, A.; Pancucci, A.; Theocharis, A.; Papathanassiou, E. Global climate change amplifies the entry of tropical species into the Eastern Mediterranean Sea. Limnol. Oceanogr. 2010, 55, 1478–1484. [Google Scholar] [CrossRef]
  22. Kalogirou, S.; Azzurro, E.; Bariche, M. The Ongoing Shift of Mediterranean Coastal Fish Assemblages and the Spread of Non-Indigenous Species. In Biodiversity Enrichment in a Diverse World; IntechOpen: London, UK, 2012. [Google Scholar]
  23. Cinar, M.E.; Bilecenoglu, M.; Ozturk, Β.; Katagan, Τ.; Yokes, Μ.Β.; Aysel, V.; Dagli, E.; Acik, S.; Ozcan, T.; Erdogan, H. An updated review of alien species on the coasts of Turkey. Mediterr. Mar. Sci. 2011, 12, 257–315. [Google Scholar] [CrossRef]
  24. Golani, D. The Sandy Shore of the Red Sea-Launching Pad for Lessepsian (Suez Canal) Migrant Fish Colonizers of the Eastern Mediterranean. J. Biogeogr. 1993, 20, 579–585. [Google Scholar] [CrossRef]
  25. Galil, B.S.; Mienis, H.K.; Hoffman, R.; Goren, M. Non-indigenous species along the Israeli Mediterranean coast: Tally, policy, outlook. Hydrobiologia 2021, 848, 2011–2029. [Google Scholar] [CrossRef]
  26. Por, F.D. Lessepsian Migration: The Influx of Red Sea Biota into the Mediterranean by Way of the Suez Canal; Springer: Berlin/Heidelberg, Germany, 1978. [Google Scholar] [CrossRef]
  27. Stern, N.I.R.; Paz, G.U.Y.; Yudkovsky, Y.; Lubinevsky, H.; Rinkevich, B. The arrival of a second ‘Lessepsian sprinter’? A first record of the red cornetfish Fistularia petimba in the Eastern Mediterranean. Mediterr. Mar. Sci. 2018, 18, 524–528. [Google Scholar] [CrossRef]
  28. Ragheb, E. Morphometric and meristic characteristics of the first record Fistularia petimba (Lacepède, 1803) and Fistularia commersonii (Rüppell, 1838) (Piscès: Fistulariidae) from the Egyptian Mediterranean waters (West Alexandria). Egypt. J. Aquat. Res. 2022, 48, 143–150. [Google Scholar] [CrossRef]
  29. Fritzsche, R.A. A Review of the Cornetfishes, Genus Fistularia (Fistulariidae), with a Discussion of Intrageneric Relationships and Zoogeography. Bull. Mar. Sci. 1976, 26, 106–204. [Google Scholar]
  30. Fischer, W.; Bianchi, G.; Fisheries and Aquaculture Management Division. FAO Species Identification Sheets for Fishery Purposes. Western Indian Ocean: Fishing Area 51; Fischer, W., Bianchi, G., Eds.; FAO: Rome, Italy, 1984. [Google Scholar]
  31. Sánchez-Tocino, L.; Hidalgo, F.; Pontes, M. Primera cita de Fistularia commersonii Ruppell, 1838 (Osteichtyes: Fistulariidae) en aguas mediterráneas de la Península Ibérica. Zool. Baetica 2007, 18, 79–84. [Google Scholar]
  32. Kalogirou, S.; Corsini-Foka, M.; Kondylatos, G.; Wennhage, H. Diet of the invasive piscivorous fish Fistularia commersonii in a recently colonized area of eastern Mediterranean. Biol. Invasions 2007, 9, 887–896. [Google Scholar] [CrossRef]
  33. Bañón, R.; Sande, C. First record of the red cornetfish Fistularia petimba (Syngnathiformes: Fistularidae) in Galician waters: A northernmost occurrence in the eastern Atlantic. J. Appl. Ichthyol. 2008, 24, 106–107. [Google Scholar] [CrossRef]
  34. Cárdenas, S.; Alvarez-Berastegui, D.; Ortiz, J.M. First record of Fistularia petimba Laccepéde, 1803 (Pisces FIstulariidae) off the coast of Cadiz (southern Iberian Peninsula). Boletín Inst. Español Oceanogr. 1997, 13, 83–86. [Google Scholar]
  35. Ünlüoğlu, A.; Akalın, S.; Dal, İ.; Tıraşın, E.; Aydın, C. First record of red cornetfish Fistularia petimba (Syngnathiformes: Fistulariidae) from Antalya and İskenderun Bays along Turkish coasts of the Mediterranean Sea. J. Appl. Ichthyol. 2018, 34, 977–980. [Google Scholar] [CrossRef]
  36. Soydemir Çiftçi, N.; Ayas, D.; Doğangün, M. New locality record for Fistularia petimba Lacepède, 1803 from the Northeastern Mediterranean Sea (Mersin Bay). 2019. Available online: https://dergipark.org.tr/en/pub/medfar/issue/45471/491571 (accessed on 9 January 2024).
  37. Karan, S.; Uyan, A.; Doğdu, S.; Gürlek, M.; Ergüden, D.; Turan, C. Genetic confirmation of Red cornetfish, Fistularia petimba (Syngnathiformes: Fistularidae) occurrence in Turkish marine waters. FishTaxa 2019, 4, 125–129. [Google Scholar]
  38. Esri. ArcGIS Online | Cloud-Based GIS Mapping Platform. 2018. Available online: https://www.esri.com/en-us/arcgis/products/arcgis-online/overview (accessed on 16 April 2024).
  39. Floerl, O.; Inglis, G.J. Starting the invasion pathway: The interaction between source populations and human transport vectors. Biol. Invasions 2005, 7, 589–606. [Google Scholar] [CrossRef]
  40. Ferrario, J.; Caronni, S.; Occhipinti-Ambrogi, A.; Marchini, A. Role of commercial harbours and recreational marinas in the spread of non-indigenous fouling species. Biofouling 2017, 33, 651–660. [Google Scholar] [CrossRef]
  41. Drake, J.M.; Lodge, D.M. Global hot spots of biological invasions: Evaluating options for ballast–water management. Proc. R. Soc. London. Ser. B Biol. Sci. 2004, 271, 575–580. [Google Scholar] [CrossRef] [PubMed]
  42. Galil, B.S.; Boero, F.; Campbell, M.L.; Carlton, J.T.; Cook, E.; Fraschetti, S.; Gollasch, S.; Hewitt, C.L.; Jelmert, A.; Macpherson, E.; et al. ‘Double trouble’: The expansion of the Suez Canal and marine bioinvasions in the Mediterranean Sea. Biol. Invasions 2015, 17, 973–976. [Google Scholar] [CrossRef]
  43. Ulman, A.; Ferrario, J.; Occhipinti, A.; Arvanitidis, C.; Bandi, A.; Bertolino, M.; Bogi, C.; Chatzigeorgiou, G.; Çiçek, B.; Içek, C.; et al. A massive update of non-indigenous species records in Mediterranean marinas. PeerJ 2017, 5, e3954. [Google Scholar] [CrossRef] [PubMed]
  44. Katsanevakis, S.; Wallentinus, I.; Zenetos, A.; Leppäkoski, E.; Çinar, M.E.; Oztürk, B.; Grabowski, M.; Golani, D.; Cardoso, A.C. Impacts of invasive alien marine species on ecosystem services and biodiversity: A pan-European review. Aquat. Invasions 2014, 9, 391–423. [Google Scholar] [CrossRef]
  45. Saad, A.A.; Sabour, W.G. Impact of invasive species on the biodiversity and fish stock; case study: Fistularia commersonii Ruppel, in the Syrian coast. Rapp. Comm. Int. Mer Médit. 2010, 39, 625. [Google Scholar]
  46. Papageorgiou, M.; Resaikos, V.; Petrou, A. A preliminary assessment of Fistularia petimba (Lacepède, 1803) migration in the Mediterranean Sea: Historical and new data from Cyprus (Levantine Sea) with biological notes. Mediterr. Mar. Sci. 2023, 24, 446–453. [Google Scholar] [CrossRef]
  47. Crocetta, F.; Al Mabruk, S.A.A.; Azzurro, E.; Bakiu, R.; Bariche, M.; Batjakas, I.E.; Bejaoui, T.; Ben Souissi, J.; Cauchi, J.; Corsini-Foka, M.; et al. “New Alien Mediterranean Biodiversity Records” (November 2021). Mediterr. Mar. Sci. 2021, 22, 724–746. [Google Scholar] [CrossRef]
  48. Chirine, H.; Ibrahim, A.; Alshawy, F. First record of Red cornetfish, Fistularia petimba Lacepède, 1803 (Actinopterygii: Fistulariidae) from the Syrian coast. Int. J. Aquat. Biol. 2019, 7, 175–179. [Google Scholar] [CrossRef]
  49. Ibrahim, A.; Alshawy, F.; Hussein, C. Confirmation records and new distribution of the red cornet fish Fistularia petimba lacepède, 1803 (actinopterygii: Fistulariidae) in the Syrian Marine Waters (Eastern Mediterranean). Species 2020, 21, 95–100. [Google Scholar]
  50. Dragicevic, B.; Anadoli, O.; Angel, D.; Benabdi, M.; Bitar, G.; Castriota, L.; Crocetta, F.; Deidun, A.; Dulčić, J.; Edelist, D.; et al. New Mediterranean Biodiversity Records (December 2019). Mediterr. Mar. Sci. 2019, 20, 645–656. [Google Scholar] [CrossRef]
  51. Cerim, H.; Yapıcı, S.; Gülşahin, A.; Soykan, O.; Bilge, G. The First Record of the Red Cornetfısh (Fistularia petimba Lacepède, 1803) in the Aegean Sea. Düzce Üniversitesi Bilim Teknol. Derg. 2021, 9, 607–615. [Google Scholar] [CrossRef]
Fishes 09 00237 g001
Figure 1. Map of the Amorgos Island, Central Aegean Sea, Greece. The red line marks the sampling area around Amorgos Island.
Figure 1. Map of the Amorgos Island, Central Aegean Sea, Greece. The red line marks the sampling area around Amorgos Island.
Fishes 09 00237 g001
Fishes 09 00237 g002
Figure 2. GNS mesh size arrangement in this study.
Figure 2. GNS mesh size arrangement in this study.
Fishes 09 00237 g002
Fishes 09 00237 g003
Figure 3. GTR mesh size arrangement in this study.
Figure 3. GTR mesh size arrangement in this study.
Fishes 09 00237 g003
Fishes 09 00237 g004
Figure 4. Fistularia petimba individual from Amorgos Island and its identification characteristics: (a) reddish colour and (b) elongated bony plates embedded in the skin.
Figure 4. Fistularia petimba individual from Amorgos Island and its identification characteristics: (a) reddish colour and (b) elongated bony plates embedded in the skin.
Fishes 09 00237 g004
Fishes 09 00237 g005
Figure 5. Records of Fistularia petimba in the Mediterranean Sea (Table 2) [38].
Figure 5. Records of Fistularia petimba in the Mediterranean Sea (Table 2) [38].
Fishes 09 00237 g005
Table 1. Morphometric characteristics and measurements of Fistularia petimba from Amorgos Island, Greece.
Table 1. Morphometric characteristics and measurements of Fistularia petimba from Amorgos Island, Greece.
MorphometricsMeasurement (mm)
Total Length without filament (TL)395.00
Total Length with filament (TLf)530.00
Filament Length (fL)124.23
Standard Length (SL) 378.00
Fork Length (FL)383.00
Body Deth (BD)7.98
Head Length (HL)142.00
Eye Diameter (ED)10.97
Snout Length (SN)114.00
Dorsal Fin Length (DFL)15.41
Dorsal Fin Height (DFH)28.89
Pectoral Fin Length (PFL)6.66
Pelvic Fin Height (PFH)16.81
Dorsal Fin Length (PvFL)2.54
Pelvic Fin Height (PvFH)6.83
Caudal Fin Length (CFL)19.01
Caudal Fin Height (CFH)5.10
Anal Fin Length (AFL)15.16
Anal Fin Height (AFH)27.37
Pre-dorsal Fin Length (pDFL)67.00
Pre-pectoral Fin Length (pPFL)319.00
Pre-pelvic Fin Length (pPvFL)190.00
Pre-anal Fin Length (pAFL)310.00
Table 2. Data of the 32 validated records of Fistularia petimba in the Mediterranean Sea.
Table 2. Data of the 32 validated records of Fistularia petimba in the Mediterranean Sea.
NoLocationLatitudeLongitudeDate (Capture)Depth (m)Gear TypeSample Size
1Cadiz, Spain [34]36.455097−4.70337223 June 199650Gillnet1
2Antalya Bay, Turkey [35]36.79355631.20916728 October 201635–43Bottom trawl1
3Ashdod, Israel [27]31.81395034.45971712 November 201680Bottom trawl1
4Antalya Bay, Turkey [35]36.73741731.43436126 November 201630Bottom trawl1
5Iskenderun, Turkey [35]36.65440036.18618321 May 201735–38Bottom trawl2
6Tripoli, Lebanon [47]34.41000035.77000015 November 2017N/AGillnet1
7Mersin Bay, Turkey [37]36.12883333.52066722 November 201795Bottom trawl1
8Antalya Bay, Turkey [37]36.06186732.5342339 January 201870Bottom trawl2
9Büyükeceli Coast (Mersin Bay) Turkey [36]36.12313933.4679445 October 2018150Bottom trawl2
10Egypt [28]El-Hamam—Sidi Kirayr.9 March 201940–60Bottom trawl1
11Lattakia, Syria [48]35.51832535.71349229 July 201945Gillnet1
12Lattakia, Syria [49]35.24308635.92000024 September 201930Gillnet1
13Gialia, Cyprus [50]35.11000032.49000026 September 201955Gillnet1
14Banyas, Syria [49]35.51832535.71349229 September 201945Gillnet2
15Gökova Bay, Turkey [51]36.85788927.89655619 October 201915–20Longline1
16Güllük Bay, Turkey [51]36.85788327.89656117 November 201965Bottom trawl4
17Cyprus [46]34.74736733.46340014 July 202055Bottom trawl3
18Cyprus [46]34.96450034.96450015 July 202048Bottom trawl1
19Cyprus [46] 34.75961733.48065016 July 202033Bottom trawl1
20Cyprus [46]34.92410033.90805024 July 202079Bottom trawl11
21Cyprus [46]35.08173332.45870024 July 202043Bottom trawl29
22Cyprus [46]34.63571732.63851727 March 202146Bottom trawl10
23Cyprus [46]34.66130032.46865027 March 202193Bottom trawl4
24Bandirma Bay, Turkey [47]40.41695028.08400011 June 202132Trammel net1
25Cyprus [46]34.69398333.1355674 August 202144Bottom trawl26
26Samos, Greece [47]37.70658326.7087837 November 202120Trammel net1
27Cyprus [46] 35.06083334.0543838 August 202186Bottom trawl4
28Cyprus [46] 34.75091733.4809338 August 202155Bottom trawl7
29Cyprus [46] 34.75091733.4809338 August 202133Bottom trawl2
30Cyprus [46] 34.69226733.1667508 August 202156Bottom trawl1
31Cyprus [46] 34.69933333.31181713 September 202113Trammel net1
32Amorgos, Greece (current study)36.8276028125.8587992228 May 202324.5–30.6Trammel net1
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Tsaousi, N.; Kalogirou, S. First Record of the Red Cornetfish Fistularia petimba Lacepède, 1803 from Amorgos Island (Central Aegean Sea; Greece) and a Review of Its Current Distribution in the Mediterranean Sea. Fishes 2024, 9, 237. https://doi.org/10.3390/fishes9060237

AMA Style

Tsaousi N, Kalogirou S. First Record of the Red Cornetfish Fistularia petimba Lacepède, 1803 from Amorgos Island (Central Aegean Sea; Greece) and a Review of Its Current Distribution in the Mediterranean Sea. Fishes. 2024; 9(6):237. https://doi.org/10.3390/fishes9060237

Chicago/Turabian Style

Tsaousi, Nefeli, and Stefanos Kalogirou. 2024. "First Record of the Red Cornetfish Fistularia petimba Lacepède, 1803 from Amorgos Island (Central Aegean Sea; Greece) and a Review of Its Current Distribution in the Mediterranean Sea" Fishes 9, no. 6: 237. https://doi.org/10.3390/fishes9060237

APA Style

Tsaousi, N., & Kalogirou, S. (2024). First Record of the Red Cornetfish Fistularia petimba Lacepède, 1803 from Amorgos Island (Central Aegean Sea; Greece) and a Review of Its Current Distribution in the Mediterranean Sea. Fishes, 9(6), 237. https://doi.org/10.3390/fishes9060237

Article Metrics

Back to TopTop