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The development of morpho-anatomical abnormalities in fish was first figured in the 16th and 17th centuries (1555–1642, Gudger, 1936). In his extensive literature review, Dawson (1964) reported 1020 publications on the presence of morpho-anatomical abnormalities (including skeletal, non-skeletal, and pigmentation defects) in wild fish. A few years later, the same author updated this literature list with 213 new publications, 137 of which were published between 1965 and 1970 (Dawson, 1971). Since then, reports on the presence of skeletal abnormalities in wild fish populations are getting more frequent. This might be attributed to the effects of anthropogenic pressures (e.g., pollution, eutrophication) on the stocks (Boglione, 2020; Diggles, 2013; García-Gasca et al., 2016; Leone et al., 2021; Messaoudi, Deli, et al., 2009), to the exponential increase of scientific awareness about this issue, as well as to the increasing amount of research on bone deformities in aquaculture and the significant research being undertaken to understand the causes (e.g., Boglione et al., 2013; Ytteborg et al., 2012). Generally, the literature on deformed fish is prevailed by records of one to a few individuals occasionally observed in the field (e.g., Grimaldi Jawad Yamamoto et al., 2013). Existing studies document that these rates may elevate to high levels, varying among the species (e.g., 11% in Labrus bergylta vs. 57% in Cyclopterus lumpus, Fjelldal et al., 2021; 9% in Liza aurata vs. 21% in Chelon labrosus, Boglione et al., 2006), and the study area (e.g., 29% in polluted vs 3% in unpolluted sites, Aphanius fasciatus, Kessabi, Annabi, et al., 2013; Kessabi, Said, 12%–16% in polluted vs. 2%–9% in unpolluted estuaries, García-Gasca et al., 2016). Studies on reared fish demonstrate that skeletal abnormalities have significant adverse effects on fish form and function (i.e., growth and survival rates, susceptibility to diseases) (reviewed by Boglione et al., 2013). Since these effects are expected to be magnified in the wild, skeletal abnormalities may constitute a significant factor of natural mortality and present a decreasing prevalence with fish age (Kessabi et al., 2009; Pollock, 2015). The status of abnormality prevalence in the wild fish of the Mediterranean Sea remains unknown. As a result, there are no reference data for future monitoring programs and the effect of fish abnormalities on stock natural mortality cannot be estimated. Existing studies on skeletal abnormalities in Mediterranean fishes have primarily focused on the use of fish abnormalities as bioindicators to assess the environmental quality of specific Italian lagoons (Boglione et al., 2006; Leone et al., 2021) and polluted areas in the Gulf of Gabes in Tunisia (Kessabi et al., 2009; Kessabi, Annabi, et al., 2013; Kessabi, Said, Messaoudi, Deli, et al., 2009; Messaoudi, Kessabi, et al., 2009). In each of these cases, the results consistently endorse the feasibility of monitoring abnormalities in fish as a viable method for promptly identifying anthropogenic influences in the Mediterranean Sea. In the present study, we report the presence of different types of skeletal abnormalities in specimens of 10 fish species from the Aegean Sea. Estimations of abnormality prevalence are provided for seven species, whereas for three species we provide only single abnormality records. Fish samples were collected in Chania area (Crete, South Aegean Sea, Greece, Figure 1), both from recreational and commercial small-scale fisheries. Fish were transferred to the laboratory and digital images of the left side of each individual were captured. All specimens were then stored at −20°C (Laboratory of Marine Biology, Biology Department, University of Crete). Fish radiography was performed by using a Mex + 60 x-ray generator (medical ECONET GmbH, Oberhausen, Germany, 40–44 kV, 1.0–1.2 mA s, 75 cm focal distance) and a Dura-line XD 14 wireless DR detector (AGFA, Mortsel, Belgium). A total of nine types of skeletal abnormalities were detected on jaws, vertebral column, dorsal and caudal fins, at rates of 3.3%–28.6% (Table 1). Vertebral abnormalities consisted of lordosis (V-shape bending of the vertebral column), kyphosis (Λ-shape bending of the vertebral column) and kypholordosis (concurrent lordosis and kyphosis) (Figures 2 and 3). In the studied Boops boops (Linnaeus, 1758) specimens, vertebral abnormalities consisted exclusively of kypholordosis (4.2%–10.3%), without any deviation from the normal meristic counts of the vertebrae and their processes (24 vertebrae) (Figure 2a,b). A single specimen of Mullus surmuletus (Linnaeus, 1758) presented concurrently three lordotic areas along its vertebral column (Figure 2c). Axis abnormalities in Sparisoma cretense (Linnaeus, 1758) (3.7%, Table 1) consisted of kyphosis of the haemal vertebral area, which was accompanied by an abnormally straightened anteriormost part of the axis, an upward shift of the skull (stargazer) and depressions of the dorsal profile of the body (Figure 2d,d′,e). A similar upward shift of the skull and depressions of the dorsal profile were observed in Pterois miles (Bennett, 1828) with lordosis (4.0%, Table 1) of the causal peduncle (Figure 3a,b). In this specimen, lordosis was associated with a fusion of the pre-ural centra 2 and 3 (PU2, PU3) into one bearing two haemal processes (Figure 3a′,b′). Finally, a Serranus scriba (Bennett, 1828) specimen (3.3%, Table 1) was recorded to present lordosis of the prehaemal area, linked with an upward shift of the skull (stargazer) (Figure 3c,d). Of the vertebral abnormalities recorded in the present study, kypholordosis is probably the most frequently reported in the wild fish (e.g., Bengtsson et al., 1985; Bensaada et al., 2023; Jawad et al., 2017; Jawad Mariasingarayan et al., 2022; Van Den Avyle et al., 1989). On the other hand, to our knowledge, this is the first record of severe lordosis of the caudal peduncle, and of the abnormally straightened anteriormost part of the axis in natural fish populations. In the present study, recorded skull abnormalities consisted of the compression of the ethmoid area and upper jaws (pugheadedness), shortened lower jaw, missing premaxillaries and lateral misalignment of the upper and lower jaws (crossbite). The highest frequency of pugheadedness was observed in one Diplodus sargus (Linnaeus, 1758) sample (28.6%, Table 1, Figure 4a–c). Pugheadedness and shortened lower jaw were present in both the examined samples of Pagellus erythrinus (Linnaeus, 1758) (Figure 4d–g), with equal frequencies (1.8%–2.8% for each abnormality type, Table 1). In one P. erythrinus specimen, pugheadedness was accompanied by crossbite (Figure 4e,e′). Missing premaxillaries were observed in one kypholordotic specimen of B. boops (Figure 4h). Of the skull abnormalities recorded in the present study, pugheadedness is the most frequently reported in wild fish (Bueno et al., 2015; Jawad et al., 2017; Näslund Porta Fragkoulis et al., 2018), but rarely in wild fish. In the present study, recorded fin abnormalities mainly consisted of the partial-to-complete lack of the dorsal fin, and/or depressions of the dorsal profile of the body (saddleback syndrome) (four species, Table 1). In one specimen of Siganus rivulatus Forsskål Cobcroft Fragkoulis et al., 2017; Koumoundouros et al., 2001) and in wild fish populations globally (e.g., in 10 species by Browder et al., 1993; in S. cretense by Koumoundouros, 2008; in Acanthopagrus australis by Diggles, 2013; Pollock, 2015; in 10 species by Jawad in Parastromateus niger by Silambarasan et al., 2021; in Lates calcarifer by Abed et al., 2023). Notably, Diggles (2013) documented an approximately sixfold increase in the prevalence of SBS among wild A. australis over a span of 20 years. The missing part of dorsal profile in S. tinca (present study) is similar to the abnormality reported in P. miles, which was attributed to physical injuries related to failed spearfishing attempts (Jimenez et al., 2022). Skeletal abnormalities in fish may be induced by unfavourable environmental and nutritional conditions (reviewed by Boglione et al., 2013), genetic factors (e.g., Fragkoulis et al., 2020; Takeuchi, 1966; Tave et al., 1983), diseases (Ngo et al., 2024; Pasnik et al., 2007; Piamsomboon et al., 2022), pollutants (e.g., Johnson et al., 2020; Kessabi, Annabi, et al., 2013; Kessabi, Said, Messaoudi, Deli, et al., 2009), or toxins from harmful algal blooms (Sergi et al., 2022). In the present study, differences in abnormality rates and types among the studied species might be related to differences in life mode, feeding habits, reproduction pattern and seasonality. For example, B. boops juveniles migrate to the anthropogenically modified littoral zone (e.g., small harbours) (Georgiadis et al., 2014), where they may be subjected to various environmental stressors. A substantial number of abnormal specimens was collected by the present study in two small marinas. The high abnormality rates observed in the case of kypholordosis in B. boops (10.3%) and pugheadedness in D. sargus (28.6%) (Table 1), might be the result of localized causative factors, but also of the aggregation of deformed individuals in a protected environment where predation pressure is lower than in the open sea. Publications reporting the presence of skeletal abnormalities in wild fish have been increasing in recent years. Since several of these abnormalities have significant adverse effects on fish performance (e.g., swimming, feeding), they could be considered as an additional source of mortality for natural stocks. However, the current available information does not allow for an estimation of the magnitude of the problem. This is mainly due to the lack of relevant monitoring surveys conducted at both spatial and temporal levels, which should also involve sampling at different developmental periods. Dimitrios Chatzakis: Investigation; formal analysis. Roula Al Belbeisi: Investigation; formal analysis. Soultana Karagianni: Investigation; formal analysis. Eustratios Karagiannakidis: Visualization; methodology. George Koumoundouros: Formal analysis; writing – review and editing; writing – original draft; conceptualization; supervision. We would like to thank M. Bastouna for her contribution to fish radiography. This study was funded by the Property Development and Management Company of the University of Crete (Project no: 98). The authors declare no conflict of interest. The data that support the findings of this study are available from the corresponding author upon reasonable request.
Chatzakis et al. (Sat,) studied this question.