Next Article in Journal
Trans-Media Kinematic Stability Analysis for Hybrid Unmanned Aerial Underwater Vehicle
Next Article in Special Issue
Estimation of Stock Status Using the LBB and CMSY Methods for the Indian Salmon Leptomelanosoma indicum (Shaw, 1804) in the Bay of Bengal, Bangladesh
Previous Article in Journal
Genotoxic Properties of Polystyrene (PS) Microspheres in the Filter-Feeder Mollusk Mytilus trossulus (Gould, 1850)
Previous Article in Special Issue
Strengthening Angel Shark Conservation in the Northeastern Mediterranean Sea
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
JMSE
Volume 10
Issue 2
10.3390/jmse10020274
jmse-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:
Article

Meridionalization as a Possible Resource for Fisheries: The Case Study of Caranx rhonchus Geoffroy Saint-Hilaire, 1817, in Southern Italian Waters

by
Salvatore Coco
1,2,*,
Alessandra Roncarati
1,
Francesco Tiralongo
2,3 and
Alberto Felici
1,*
1
School of Biosciences and Veterinary Medicine, University of Camerino, Viale Circonvallazione 93-95, 62024 Matelica, Italy
2
Ente Fauna Marina Mediterranea, Scientific Organization for Research and Conservation of Marine Biodiversity, 96012 Avola, Italy
3
Department of Biological, Geological and Environmental Sciences, University of Catania, 95124 Catania, Italy
*
Authors to whom correspondence should be addressed.
J. Mar. Sci. Eng. 2022, 10(2), 274; https://doi.org/10.3390/jmse10020274
Submission received: 3 December 2021 / Revised: 7 February 2022 / Accepted: 15 February 2022 / Published: 16 February 2022
(This article belongs to the Special Issue Coastal Fish Research II)
Browse Figures
Review Reports Versions Notes

Abstract

:
Climate change affects the shift range distribution of species, especially among mobile species, and this phenomenon can alter ecosystems and impacts human activities. Fishing is an anthropic activity that undergoes the effect not only of the introduction and increase of non-native species but also of native thermophilic ones. Some of these species can become a commercially exploitable resource. However, this information is often obscured by the negative effects these species can cause to the environment. We investigated how the thermophilic species Caranx rhonchus, neglected in Italy, could become a relevant resource. We studied the nutritional profile and the presence of heavy metal contamination and compared these traits with those of a similar common Mediterranean species, namely Trachurus trachurus. The proximate composition was determined following the AOAC procedure, while the fatty acid profile was determined by GC/MS, and the mineral component was obtained by mass spectrometer (ICP-MS). Caranx rhonchus is a nutritionally good species, although it is little consumed and exploited. Increasing the market supply with new commercially exploitable emerging species would benefit local communities and the environment. Therefore, it is necessary to investigate how a shift of the range caused by climate change can provide benefits within the human dimension.

1. Introduction

The Mediterranean Sea is one of the most vulnerable areas to climate change, with dramatic effects favoring the spread of non-indigenous and thermophilic native species [1,2]. In particular, the range shift of species in the Mediterranean Sea is caused by two distinct phenomena: tropicalization, with non-indigenous species introduced by human activities (e.g., Suez Canal and ballast waters) [1], and meridionalization, with the northwards expansion of species usually restricted to the warmer southern part of the Mediterranean Sea [3]. The increase in water temperature has triggered rapid shifts in the range distribution of species [4,5,6]. These shifts have a direct effect on different habitats by reshaping local biocommunities [7,8], and on human activities [9]. Fisheries undertake an anthropic activity strongly affected by the shifting range distribution of aquatic species [10,11,12,13], with repercussions along social and economic dimensions of these social-ecological systems [14,15]. On the other hand, some Mediterranean fisheries have benefited from the presence of these species [16,17]. Indeed, many non-native species have become targets for fisheries, [18,19,20] and several Mediterranean fisheries have become dependent on the economic returns from the fishing of these species [18,21,22]. Many studies highlight the negative effects caused by the expansion of non-native invasive species, such as pest introduction [23,24], economic damage [25,26], and health risks [27,28,29]. Simultaneously, although rarely documented, non-native species can also contribute to the local economy by becoming a new resource, e.g., food [30]. Some of these species may become targets of local fisheries [31,32] but their economic benefit may be obscured by the negative impact on native species and habitats [33]. Non-native species often have a similar morphology and taste to local ones and can therefore be potentially easily commercialized. For example, the Lessepsian species Upeneus moluccensis Bleeker, 1855, and Upeneus pori Ben-Tuvia & Golani, 1989, have become highly sought-after resources due to their similarity to the two indigenous Mullidae species Mullus barbatus Linnaeus, 1758, and Mullus surmuletus Linnaeus, 1758, that are highly valued in the Mediterranean [19,34]. Another example is the species Nemipterus randalli Russell, 1986, first recorded in the Mediterranean in 2005 [32]. This species, however, was readily incorporated into markets as it is very similar in morphology and size to the native Sparids [35]. The use of non-indigenous species as human food resources can be compared for some aspects to that of neglected native ones. For example, a similar case in Italy can be seen in the false scad Caranx rhonchus Geoffroy Saint-Hilaire, 1817, a thermophilic species morphologically similar to a commercially well-known species Trachurus trachurus (Linnaeus, 1758) both caught in the same season using the same fishing techniques. In Italy, C. rhonchus is uncommon, although occasionally caught, especially along the Sicilian coasts, where it seems to have undergone a marked increase in abundance in recent years [36,37].
The false scad is a member of the family Carangidae, whose distribution extends in the eastern Atlantic, from Morocco to Namibia, and in the Mediterranean Sea, mainly along the African coast [38]. In the Gulf of Gabes (Tunisia), this fish is abundant and represents an important commercial species for fisheries [39]. However, despite its increasing abundance along Sicilian coasts (central Mediterranean Sea), this species can be considered commercially neglected, although it is occasionally present in local fish markets of south Italy, where it has a medium commercial value of EUR 10–12/kg and is sold as T. trachurus. The false scad can be considered a semi-pelagic fish, being both reported near the surface and near the bottom, along coastal marine waters (from a few meters of depth up to approximately 200 m) [38]. The false scad is an opportunistic piscivorous, whose diet partially overlaps with that of the greater amberjack, Seriola dumerili (Risso, 1810) [40]. On the other hand, it was found to be one of the main food items in the diet of the European hake, Merluccius merluccius (Linnaeus, 1758) [41].
In this study, we explored the positive opportunities provided by the phenomenon of meridionalization, analyzing the case of C. rhonchus. We acquired more information on the nutritional characteristics of the species in order to favor the regular introduction of this product among the species of consumer choice. In addition, we investigated the presence of heavy metal (and trace elements) in the meat of the species, for the assessment of the risk for human consumption. In order to facilitate the marketing of this species in Italy and in Mediterranean countries in general, the fillet quality traits of this neglected species, whose abundance is increasing in Italy, were compared with those of the Atlantic horse mackerel (T. trachurus), a well-known commercial fish species under whose name is also sold C. rhonchus, along the Sicilian coasts.

2. Materials and Methods

2.1. Samples and Sampling Areas

Samples of false scad specimens of commercial size were provided by fishermen of the small artisanal fishery that had caught them within three miles from the seashore, along the eastern coast of Sicily in front of the area located between Catania and Portopalo di Capo Passero (Figure 1), between October and December 2020. Twelve male specimens were immediately measured in weight (g) and length (cm). Measurements were performed using an electronic scale (mod. CP224S Sartorius, Gottigen, Germany) and an ictiometer. Each fish was immediately beheaded, eviscerated, and filleted. The edible part of each specimen was removed, separately homogenised, and codified; the samples were stored at −18 °C and transported in dry ice to the laboratory of Camerino University to determine the proximate composition, the fatty acid profile, and the determination of elements. The same was performed for twelve male specimens of the Atlantic horse-mackerel (T. trachurus), with similar body weight and captured in the same area. Here we provide a photographic comparison between the two species, remembering that, at the fish market, C. rhonchus is sold under the name of T. trachurus, together with true specimens of this latter species (Figure 2).

2.2. Proximate Composition

For both the species, the moisture percentage was determined following the procedure of the Association official Analytical Chemists (AOAC) [42]. Total lipid content was measured using a modification of the chloroform:methanol procedure described by [43]. Proteins were determined using the standard Kjeldahl copper catalyst method. Ash was determined using the AOAC procedure.

2.3. Fatty Acid Profile Determination

In the pool of the two fish samples, after determining the total lipid content, the fatty acids were converted to methyl esters following the method described by [44]. An Agilent Technologies GC/MS (6890N)/MSD (5973inert) system (Agilent, Palo Alto, CA, USA) equipped with a db5 column (60 mt, 0.25 mm) and calibrated was used for separation of fatty acid methyl esters. The operating conditions of the gas chromatograph were as follows: oven temperature was kept at 170 °C for 15 min, increased to 190 °C at a rate of 1 °C/min, then increased to 220 °C at a rate of 5 °C/min, and held at this temperature for 17 min. The temperature of the injector was 280 °C. Helium was used as the carrier gas at a constant flow of 1.0 mL/min. The identification of individual fatty acids was accomplished by comparing the observed retention times to fatty methyl esters of standard mixtures (37 FAME Mix, Supelco) and NIST MASS SPECTRAL DATABASE (NIST MS SEARCH 2.3) for mass spectrum.

2.4. Determination of Elements in Meat

The quantity of essential (selenium, iron, calcium, zinc, magnesium, sodium, and potassium) and non-essential elements (cadmium, chromium, mercury, cobalt, and lead) was determined using Agilent inductively coupled plasma with mass spectrometer (ICP-MS) 7800 model (Agilent, Palo Alto, CA, USA), an inductively coupled plasma with mass spectrometer (ICP-MS) system following the procedure reported by [45]. The calibration curve profiles were obtained using standard element solutions obtained by diluting the mother solution in 3% HNO3 + 0.05% HCl with yttrium, scandium, terbium, and bismuth as internal standards.

2.5. Statistical Analysis

The results concerning the proximate composition, the fatty acid profile, and the minerals of the two fish species were submitted to one-way analyses of variance (ANOVA) [46]. Differences were considered significant at p < 0.05, and means were compared using the Student-Newman-Keuls (SNK) test.

3. Results

3.1. Morphometric Parameters

Total length and standard length and weight of measured specimens of both species are reported in Table 1.

3.2. Proximate Composition and Fatty Acid Profile and Mineral Content

The proximate composition (Table 2) shows the presence of a good protein content without significant differences in both species. Lipids exhibited differences with the highest rate in the false scad compared to the Atlantic horse-mackerel. Notable differences, although very slight, were observed in the ash content. As concerns the fatty acid profile (Figure 3), the false scad showed the presence of the most representative fatty acids recorded in the Mediterranean fish, although differences were observed compared with the horse-mackerel. Among the SFA of the false scad, the most important fatty acid was represented by palmitic acid (16:0) followed by stearic acid (18:0); both the fatty acids were higher than the Atlantic horse-mackerel, and the total of SFA resulted the highest in the false scad. Among the MUFA, the false scad showed the prevalence of oleic acid (18:1) and palmitoleic acid (16:1) in proportions higher than the same fatty acids determined in the Atlantic horse-mackerel. As concerns the n-6 fatty acids, the three FA detected in the C. rhonchus were higher than the T. trachurus; however, due to the high standard deviation, the total of n-6 PUFAs resulted in similar percentages between the two fish species. In terms of n-3 PUFAs, the false scad had high proportions of EPA (20:5 n-3), resulting higher than the that determined in the Atlantic horse-mackerel, whereas DHA and DPA had a proportion lower than the Atlantic horse-mackerel. The results of the mineral contents of the edible part of C. rhonchus and T. trachurus are presented in Table 3. The false scad showed to have a mineral content and low amounts of heavy metals (Cd, Hg, and Pb) without significant differences compared with the mineral content of the T. trachurus.

4. Discussion

In this study, we have shown the potential of C. rhonchus for human consumption, providing new data on its nutritional values, trace elements, and heavy metals, satisfying the lack of information in this regard. The false scad is a thermophilic species that has increased its abundance in Italian waters [37], and in recent years it is commonly sold in fish markets, especially in those of southern Italy. Due to its similarity with species of the genus Trachurus Rafinesque, 1810, and to the fact that the species are often sold together, C. rhonchus generally goes unnoticed to consumers, who consume it as a species of the genus Trachurus. However, this species is sold under the common Italian name of “Suro imperiale” (or “Sauro imperiale”), demonstrating that fishmongers are aware that it is another species, although they consider it a Trachurus species (called “Suro” or “Sugarello”). As mentioned above, the species of the genus Trachurus and C. rhonchus are often sold together. Along the Sicilian Ionian coast, the catches of the false scad using trammel nets have increased in frequency and abundance over recent years (Tiralongo, F., personal observations, and [37]).
The comparisons of the edible parts between C. rhonchus and T. trachurus showed that the two fish species have remarkably similar nutritional profiles, especially as regards protein and mineral content. Iron, selenium, and zinc are present in quantities of interest for human consumption, while the heavy metal content is negligible in both species, not involving any risk to human health. The fat content is low in both species, but especially in T. trachurus, which also shows a higher level of n-3 PUFA fatty acids due to the higher percentage of DHA compared to C. rhonchus (27.37% and 17.51% as mean values, respectively), which shows a greater content of EPA and Arachidonic Acid. Overall, therefore, the quality traits of the false scad showed a high value due to high protein level, low lipid content, and high n-3 PUFA fatty acids.
In the central Mediterranean, specifically along the Tunisian coast, similar studies were carried out on smaller C. rhonchus individuals, weighing less than 100 g and with a length of less than 22 cm [47,48]. Comparison of the data obtained in these studies on male fish caught in the autumn shows similar values for moisture, protein, fat, and ash. Comparing the data collected by us with those reported in these studies, relating to male specimens fished in the autumn, reveals that similar values of moisture, protein, fat, and ash were detected; similarly, the content of heavy metals is also very low, while the mean value of iron is higher in our larger specimens than the smaller ones investigated in the other study (1.01 mg/100 g ww and 0.16 mg/100 g ww, respectively).
The results obtained show that C. rhonchus has high-quality nutritional properties, much like those possessed by T. trachurus. Therefore, this new emerging species has the characteristics to be valorized and marketed as well as T. trachurus, in order to implement awareness and a more sustainable exploitation of marine resources. The failure to properly exploit a species with good qualities such as C. rhonchus highlights the lack of data and consumers’ awareness on new alternative species for consumption. There is the need to acquire information on which non-native and native thermophilic species in expansion can benefit the human dimension. Moreover, it has been observed that human consumption of marine invasive species could control their population’s size [31,49,50,51].
The possibility of increasing supply with new resources makes it possible over time to lower the fishing pressure of the usual exploited species [51]. Several initiatives have already promoted the consumption of non-indigenous species, intending to inform consumers in order to turn them into a source of food and an economic benefit for local communities [52,53]. The same can also be applied to native thermophilic species, such as in the case here reported of C. rhonchus.
In conclusion, future scenarios will see the shift range of new species an increasingly common phenomenon in the Mediterranean Sea. The increasing number of non-indigenous species entering through the Suez Canal and thermophilic species entering through the Strait of Gibraltar or expanding their distribution from the southern Mediterranean Sea will change fisheries and species availability for human consumption in Mediterranean countries [1]. It is therefore necessary to understand how the shift range can benefit the human dimension and which non-indigenous and native invasive species can be commercially exploited. This is necessary for the proper management of fisheries and to guide consumers into more informed and responsible choices.

Author Contributions

Conceptualization, S.C.; methodology, A.F., A.R. and S.C.; validation, S.C., A.R. and A.F.; formal analysis, A.F. and A.R.; investigation, F.T., A.F. and S.C.; resources, F.T. and S.C.; data curation, S.C., A.F. and A.R.; writing—original draft preparation, S.C.; writing—review and editing, S.C., F.T. and A.R.; visualization, A.R., F.T. and S.C.; supervision, A.R. and A.F.; project administration, A.F. All authors have read and agreed to the published version of the manuscript.

Funding

This study was funded by the University of Camerino through the grant “Identification of alien fish species of commercial interest”, number BVA000014–224/2021 BV.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data will made available on request.

Acknowledgments

We gratefully acknowledge all artisanal fishermen, Red Fish s.r.l and Valpesce s.r.l. Mercato del Pesce Acireale who participated in this study by providing some fish specimens.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Bianchi, C.N.; Morri, C. Global Sea warming and “tropicalization” of the Mediterranean Sea: Biogeographic and ecological aspects. Biogeographia 2003, 24, 129. [Google Scholar] [CrossRef] [Green Version]
  2. Boero, F.; Féral, J.P.; Azzurro, E.; Cardin, V.; Riedel, B.; Despalatović, M.; Munda, I.; Moschella, P.; Zaouali, J.; Fonda Umani, S.; et al. I—Executive Summary of CIESM workshop climate warming and related changes in Mediterranean marine biota. In CIESM Workshop Monographs; CIESM: Bd de Suisse, Monaco, 2008; Volume 35, pp. 5–21. [Google Scholar]
  3. Azzurro, E. Commission Internationale pour l’Exploration Scientifique de la Mer Mediterranee—CIESM Monaco. The advance of thermophilic fishes in the Mediterranean Sea: Overview and methodological questions. In CIESM Workshop Monographs; CIESM: Bd de Suisse, Monaco, 2008; Volume 35, pp. 39–45. [Google Scholar]
  4. Cheung, W.W.L.; Lam, V.W.Y.; Sarmiento, J.L.; Kearney, K.; Watson, R.; Pauly, D. Projecting global marine biodiversity im-pacts under climate change scenarios. Fish Fish. 2009, 10, 235–251. [Google Scholar] [CrossRef]
  5. Simberloff, D.; Martin, J.L.; Genovesi, P.; Maris, V.; Wardle, D.A.; Aronson, J.; Courchamp, F.; Bella, G.; Garcìa-Berthou, E.; Pascal, M.; et al. Impacts of biological invasions: What’s what and the way forward. Trends Ecol. Evol. 2013, 28, 58–66. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  6. Fogarty, H.E.; Burrows, M.T.; Pecl, G.T.; Robinson, L.M.; Poloczanska, E.S. Are fish outsidetheir usual ranges early indicators of climate-driven range shifts? Glob. Chang. Biol. 2017, 23, 2047–2057. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  7. Galil, B.S.; Marchini, A.; Occhipinti-Ambrogi, A. Mare Nostrum, Mare Quod Invaditur—The History of Bioinvasions in the Mediterranean Sea, Histories of Bioinvasions in the Mediterranean; Springer: Cham, Switzerland, 2018; pp. 21–49. [Google Scholar]
  8. Galil, B.S.; Danovaro, R.; Rothman, S.B.S.; Gevili, R.; Goren, M. Invasive biota in the deep-sea Mediterranean: An emerging issue in marine conservation and management. Biol. Invasions 2019, 21, 281–288. [Google Scholar] [CrossRef] [Green Version]
  9. Shackleton, R.T.; Larson, B.M.; Novoa, A.; Richardson, D.M.; Kull, C.A. The human and social dimensions of invasion science and management. J. Environ. Manag. 2019, 229, 1–9. [Google Scholar] [CrossRef] [Green Version]
  10. Cochrane, K.; De Young, C.; Soto, D.; Bahri, T. Climate change implications for fisheries and aquaculture. FAO Fish. Aquac. Tech. Paper 2009, 530, 212. [Google Scholar]
  11. Brander, K. Impacts of climate change on fisheries. J. Mar. Syst. 2010, 79, 389–402. [Google Scholar] [CrossRef]
  12. Azzurro, E.; Sbragaglia, V.; Cerri, J.; Bariche, M.; Bolognini, L.; Ben Souissi, J.; Busoni, G.; Coco, S.; Chryssanthi, A.; Fanelli, E.; et al. Climate change, biological invasions, and the shifting distribution of Mediterranean fishes: A large-scale survey based on local ecological knowledge. Glob. Chang. Biol. 2019, 25, 2779–2792. [Google Scholar] [CrossRef] [PubMed]
  13. Plagányi, É. Climate change impacts on fisheries. Science 2019, 363, 930–931. [Google Scholar] [CrossRef]
  14. Cinner, J.E.; Huchery, C.; Darling, E.S.; Humphries, A.T.; Graham, N.A.; Hicks, C.C.; Marshall, N.; McClanahan, T.R. Eval-uating social and ecological vulnerability of coral reef fisheries to climate change. PLoS ONE 2013, 8, e74321. [Google Scholar] [CrossRef] [PubMed]
  15. Salgueiro-Otero, D.; Ojea, E. A better understanding of social-ecological systems is needed for adapting fisheries to climate change. Mar. Policy 2020, 122, 104123. [Google Scholar] [CrossRef]
  16. Kleitou, P.; Crocetta, F.; Giakoumi, S.; Giovos, I.; Hall-Spencer, J.M.; Kalogirou, S.; Kletou, D.; Moutopoulos, D.K.; Rees, S. Fishery reforms for the management of non-indigenous species. J. Environ. Manag. 2020, 280, 111690. [Google Scholar] [CrossRef]
  17. Vimercati, G.; Kumschick, S.; Probert, A.F.; Volery, L.; Bacher, S. The importance of assessing positive and beneficial impacts of alien species. NeoBiota 2020, 62, 525–545. [Google Scholar] [CrossRef]
  18. Michailidis, N.; Corrales, X.; Karachle, P.K.; Chartosia, N.; Katsanevakis, S.; Sfenthourakis, S. Modelling the role of alien spe-cies and fisheries in an Eastern Mediterranean insular shelf ecosystem. Ocean. Coast. Manag. 2019, 175, 152–171. [Google Scholar]
  19. Van Rijn, I.; Kiflawi, M.; Belmaker, J. Alien species stabilize local fisheries catch in a highly invaded ecosystem. Can. J. Fish. Aquat. Sci. 2019, 77, 752–761. [Google Scholar] [CrossRef] [Green Version]
  20. Saygu, I.; Heymans, J.J.; Fox, C.J.; Özbilgin, H.; Eryaşar, A.R.; Gökçe, G. The importance of alien species to the food web and bottom trawl fisheries of the Northeastern Mediterranean, a modelling approach. J. Mar. Syst. 2020, 202, 103253. [Google Scholar] [CrossRef]
  21. Corrales, X.; Coll, M.; Ofir, E.; Heymans, J.J.; Steenbeek, J.; Goren, M.; Edelist, D.; Gal, G. Future scenarios of marine resources and ecosystem conditions in the Eastern Mediterranean under the impacts of fishing, alien species and sea warming. Sci. Rep. 2018, 8, 14284. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  22. 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]
  23. El-Sayed, A.M.; Suckling, D.M.; Byers, J.A.; Jang, E.B.; Wearing, C.H. Potential of “lure and kill” in long-term pest management and eradication of invasive species. J. Econ. Entomol. 2009, 102, 815–835. [Google Scholar] [CrossRef]
  24. Boussellaa, W.; Neifar, L.; Goedknegt, A.; Thieltges, D.W. Lessepsian migration and parasitism: Richness, prevalence and intensity of parasites in the invasive fish Sphyraena chrysotaenia compared to its native congener Sphyraena sphyraena in Tunisian coastal waters. PeerJ 2018, 6, e5558. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  25. Connelly, N.A.; O’neill, C.R.; Knuth, B.A.; Brown, T.L. Economic Impacts of Zebra Mussels on Drinking Water Treatment and Electric Power Generation Facilities. Environ. Manag. 2007, 40, 105–112. [Google Scholar] [CrossRef] [PubMed]
  26. Ünal, V.; Göncüoğlu, H.; Durgun, D.; Tosunoğlu, Z.; Deval, M.C.; Turan, C. Silver-cheeked toadfish, Lagocephalus sceleratus (Actinopterygii: Tetraodontiformes: Tetraodontidae), causes a substantial economic losses in the Turkish Mediterranean coast: A call for decision makers. Acta Ichthyol. Piscat. 2015, 15, 231–237. [Google Scholar] [CrossRef] [Green Version]
  27. Medlock, J.M.; Hansford, K.M.; Schaffner, F.; Versteirt, V.; Hendrickx, G.; Zeller, H.; Van Bortel, W. A Review of the Invasive Mosquitoes in Europe: Ecology, Public Health Risks, and Control Options. Vector-Borne Zoonotic Dis. 2012, 12, 435–447. [Google Scholar] [CrossRef] [Green Version]
  28. Galil, B. Poisonous and venomous: Marine alien species in the Mediterranean Sea and human health. Invasive Species Hum. Health 2018, 3, 1–15. [Google Scholar] [CrossRef]
  29. Bédry, R.; de Haro, L.; Bentur, Y.; Senechal, N.; Galil, B. Toxicological risks on the human health of populations living around the Mediterranean Sea linked to the invasion of non-indigenous marine species from the Red Sea: A review. Toxicon 2021, 191, 69–82. [Google Scholar] [CrossRef]
  30. Nuñez, M.A.; Kuebbing, S.; Domarco, R.D.; Simberloff, D. Invasive species: To eat or not to eat, that is the question. Conserv. Lett. 2012, 5, 334–341. [Google Scholar] [CrossRef]
  31. Tom, M.; Shlagman, A.; Lewinsohn, C. The benthic phase of the life cycle of Penaeus semisulcatus De Haan (Crustacea De-capoda) along the southeastern coast of the Mediterranean. Mar. Ecol. 1984, 5, 229–241. [Google Scholar] [CrossRef]
  32. Stern, N.; Levitt, Y.; Galil, B.S.; Diamant, A.; Yokeş, M.B.; Goren, M. Distribution and population structure of the alien Indo-Pacific Randall’s threadfin bream Nemipterus randalli in the eastern Mediterranean Sea. J. Fish Biol. 2014, 85, 394–406. [Google Scholar] [CrossRef] [PubMed]
  33. Ogutu-Ohwayo, R. The decline of the native fishes of lakes Victoria and Kyoga (East Africa) and the impact of introduced species, especially the Nile perch, Lates niloticus, and the Nile tilapia, Oreochromis niloticus. J. Appl. Phycol. 1990, 27, 81–96. [Google Scholar] [CrossRef]
  34. Papaconstantinou, C.; Farrugio, H. Fisheries in the Mediterranean. Mediterr. Mar. Sci. 2000, 1, 5–18. [Google Scholar] [CrossRef]
  35. Yapici, S.; Filiz, H. Biological aspects of two coexisting native and non-native fish species in the Aegean Sea: Pagellus erythrinus vs Nempterus randalli. Mediterr. Mar. Sci. 2019, 20, 594–602. [Google Scholar] [CrossRef]
  36. Costa, F. Atlante dei Pesci dei Mari Italiani; Gruppo Ugo Mursia Editore; MURSIA: Milan, Italy, 1991; p. 438. [Google Scholar]
  37. Tiralongo, F.; Crocetta, F.; Riginella, E.; Lillo, A.O.; Tondo, E.; Macali, A.; Mancini, E.; Russo, F.; Coco, S.; Paolillo, G.; et al. Snapshot of rare, exotic and overlooked fish species in the Italian seas: A citizen science survey. J. Sea Res. 2020, 164, 101930. [Google Scholar] [CrossRef]
  38. Froese, R.; Pauly, D. (Eds.) FishBase 2000: Concepts Designs and Data Sources; WorldFish: Penang, Malaysia, 2000; Volume 1594. [Google Scholar]
  39. Sley, A.; Jarboui, O.; Ghorbel, M.; Bouain, A. Diet composition and food habits of Caranx rhonchus (Carangidae) from the Gulf of Gabes (central Mediterranean). J. Mar. Biol. Assoc. UK 2008, 88, 831–836. [Google Scholar] [CrossRef]
  40. Fischer, W.; Bauchot, M.L.; Schneider, M. Fiches de la FAO d’identification des especes pour les besoins de la pêche (Révision 1) Méditerranée et Mer Noire. Zone Pêche 1987, 37, 761–11530. [Google Scholar]
  41. Philips, A.E. Feeding behavior of the European hake Merluccius merluccius Linnaeus, 1758 (Family: Gadidae) from Egyptian Mediterranean waters off Alexandria. Egypt. J. Aquat. Res. 2012, 38, 39–44. [Google Scholar] [CrossRef] [Green Version]
  42. Association of Official Analytical Chemists. Meat and meat products. In Official Methods of Analysis, 15th ed.; Association of Official Analytical Chemists: Washington, DC, USA, 1990; Volume 2, pp. 931–948. [Google Scholar]
  43. Folch, J.; Lees, M.; Sloane Stanley, G.H. A simple method for the isolation and purification of total lipids from animal tissues. J. Biol. Chem. 1957, 60, 497–509. [Google Scholar] [CrossRef]
  44. Christopherson, S.W.; Glass, R.L. Preparation of milk methyl esters by alcoholysis in an essentially non-alcoholic solution. J. Dairy Sci. 1969, 52, 1289–1290. [Google Scholar] [CrossRef]
  45. Felici, A.; Bilandžić, N.; Magi, G.E.; Iaffaldano, N.; Fiordelmondo, E.; Doti, G.; Roncarati, A. Evaluation of Long Sea Snail Hinia reticulata (Gastropod) from the Middle Adriatic Sea as a Possible Alternative for Human Consumption. Foods 2020, 9, 905. [Google Scholar] [CrossRef] [PubMed]
  46. IBM Corp. IBM SPSS Statistics for Windows, Released; Version 25.0; IBM Corp: Armonk, NY, USA, 2017. [Google Scholar]
  47. Khitouni, K.; Abdelmouleh, I.; Bouain, A.A.; Mihoubi, N.B. Variations of the chemical compositions of five coastal catch fish species of the Gulf of Gabes (Tunisia). Cybium 2010, 34, 175–183. [Google Scholar]
  48. Khitouni, I.K.; Mihoubi, N.B.; Bouain, A.; Rebah, F.B. Accumulation of Hg, Pb, Cr, and Fe in muscle and head of four fish species: Diplodus annularis, Zosterisessor ophiocephalus, Liza aurata and Caranx rhonchus. Int. J. Adv. Biol. 2014, 5, 288. [Google Scholar]
  49. Blakeway, R.D.; Jones, G.A.; Boekhoudt, B. Controlling lionfishes (Pterois spp.) with consumption: Survey data from Aruba demonstrate acceptance of non-native lionfishes on the menu and in seafood markets. Fish. Manag. Ecol. 2019, 27, 227–230. [Google Scholar] [CrossRef]
  50. Ulman, A.; Harris Holden, E.; Doumpas, N.; Deniz Akbora, H.; Al Mabruk Sara, A.A.; Azzurro, E.; Bariche, M.; Çiçek Burak, A.; Deidun, A.; Demirel, N.; et al. Low Pufferfish and Lionfish Predation in Their Native and Invad-ed Ranges Suggests Human Control Mechanisms May Be Necessary to Control Their Mediterranean Abundances. Front. Mar. Sci. 2021, 3, 868. [Google Scholar]
  51. Penca, J.; Said, A.; Cavallé, M.; Pita, C.; Libralato, S. Sustainable small-scale fisheries markets in the Mediterranean: Weak-nesses and opportunities. Marit. Stud. 2021, 7, 1–15. [Google Scholar]
  52. Giakoumi, S.; Katsanevakis, S.; Albano, P.G.; Azzurro, E.; Cardoso, A.C.; Cebrian, E.; Deidun, A.; Edelist, D.; Francour, P.; Jimenez, C.; et al. Management priorities for marine invasive species. Sci. Total Environ. 2019, 688, 976–982. [Google Scholar] [CrossRef] [PubMed]
  53. Kleitou, P.; Savva, I.; Kletou, D.; Hall-Spencer, J.M.; Antoniou, C.; Christodoulides, Y.; Chartosia, N.; Hadjioannou, L.; Dimitriou, A.C.; Jimenez, C.; et al. Invasive lionfish in the Mediterranean: Low public awareness yet high stakeholder concerns. Mar. Policy 2019, 104, 66–74. [Google Scholar] [CrossRef]
Jmse 10 00274 g001 550
Figure 1. The image shows the sampling area; the red line indicates the area where C. rhonchus and T. trachurus were captured.
Figure 1. The image shows the sampling area; the red line indicates the area where C. rhonchus and T. trachurus were captured.
Jmse 10 00274 g001
Jmse 10 00274 g002 550
Figure 2. The image shows the comparison of the morphological differences between the two species C. rhonchus (A) and T. trachurus (B). The red arrow shows the yellow band along the body, while the red circle shows the black spot on the beginning of the second dorsal fin in C. rhonchus, both absent in T. trachurus.
Figure 2. The image shows the comparison of the morphological differences between the two species C. rhonchus (A) and T. trachurus (B). The red arrow shows the yellow band along the body, while the red circle shows the black spot on the beginning of the second dorsal fin in C. rhonchus, both absent in T. trachurus.
Jmse 10 00274 g002
Jmse 10 00274 g003 550
Figure 3. Fatty acid profile categories (% of the total fatty acids) and PUFA n-3/PUFA n-6 ratio of the two species. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05). SFA = Saturated Fatty Acids; MUFA = Monounsaturated fatty acids; PUFA = Polyunsaturated Fatty Acids.
Figure 3. Fatty acid profile categories (% of the total fatty acids) and PUFA n-3/PUFA n-6 ratio of the two species. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05). SFA = Saturated Fatty Acids; MUFA = Monounsaturated fatty acids; PUFA = Polyunsaturated Fatty Acids.
Jmse 10 00274 g003
Table
Table 1. Mean size and mean body weight sampled in the two fish species.
Table 1. Mean size and mean body weight sampled in the two fish species.
Caranx rhonchusTrachurus trachurus
Total length (cm)35.08 ± 3.727.2 ± 2.4
Standard length (cm)29.9 ± 3.69-
Total Body weight (g)372.25 ± 31.27348.06 ± 8.97
Table
Table 2. Proximate composition (g/100 g ww) of the edible part of C. rhonchus and T. trachurus. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05).
Table 2. Proximate composition (g/100 g ww) of the edible part of C. rhonchus and T. trachurus. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05).
MoistureProteinLipidsAsh
Caranx rhonchus74.99 ± 1.0120.3 ± 0.932.34 ± 0.15 a1.2 ± 0.1 b
Trachurus trachurus78.09 ± 1.3919.69 ± 0.111.09 ± 0.13 b1.59 ± 0.22 a
Table
Table 3. Trace elements and heavy metals content (mg/110 g ww) of the two species. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05).
Table 3. Trace elements and heavy metals content (mg/110 g ww) of the two species. Different letters (a, b) in the same column show differences significantly different between the means (p < 0.05).
Caranx rhonchusTrachurus trachurus
CalciumCa98 ± 7.86 b189.2 ± 4.38 a
PotassiumK537 ± 38.06 a413 ± 13.34 b
MagnesiumMg41 ± 6.6740.4 ± 1.52
SodiumNa49 ± 5.649.4 ± 2.41
IronFe1.01 ± 0.0981.59 ± 0.04
SeleniumSe0.066 ± 0.0070.128 ± 0.08
ZincZn1.31± 0.071.11 ± 0.12
CadmiumCd0.005 ± 0.0030.011 ± 0.007
MercuryHg0.03 ± 0.0020.04 ± 0.001
LeadPb0.017 ± 0.0080.022 ± 0.004
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Coco, S.; Roncarati, A.; Tiralongo, F.; Felici, A. Meridionalization as a Possible Resource for Fisheries: The Case Study of Caranx rhonchus Geoffroy Saint-Hilaire, 1817, in Southern Italian Waters. J. Mar. Sci. Eng. 2022, 10, 274. https://doi.org/10.3390/jmse10020274

AMA Style

Coco S, Roncarati A, Tiralongo F, Felici A. Meridionalization as a Possible Resource for Fisheries: The Case Study of Caranx rhonchus Geoffroy Saint-Hilaire, 1817, in Southern Italian Waters. Journal of Marine Science and Engineering. 2022; 10(2):274. https://doi.org/10.3390/jmse10020274

Chicago/Turabian Style

Coco, Salvatore, Alessandra Roncarati, Francesco Tiralongo, and Alberto Felici. 2022. "Meridionalization as a Possible Resource for Fisheries: The Case Study of Caranx rhonchus Geoffroy Saint-Hilaire, 1817, in Southern Italian Waters" Journal of Marine Science and Engineering 10, no. 2: 274. https://doi.org/10.3390/jmse10020274

APA Style

Coco, S., Roncarati, A., Tiralongo, F., & Felici, A. (2022). Meridionalization as a Possible Resource for Fisheries: The Case Study of Caranx rhonchus Geoffroy Saint-Hilaire, 1817, in Southern Italian Waters. Journal of Marine Science and Engineering, 10(2), 274. https://doi.org/10.3390/jmse10020274

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop