Natural hybridization between immigrant narrow-barred Spanish
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Animal Biodiversity and Conservation 44.2 (2021) 219 Natural hybridization between immigrant narrow–barred Spanish mackerel Scomberomorus commerson (Lacepède, 1800) and endemic West African Spanish mackerel Scomberomorus tritor (Cuvier, 1832) in the Egyptian Mediterranean coast S. A. Bakhoum Bakhoum, S. A., 2021. Natural hybridization between immigrant narrow–barred Spanish mackerel Scomberomorus commerson (Lacepède, 1800) and endemic West African Spanish mackerel Scomberomorus tritor (Cuvier, 1832) in the Egyptian Mediterranean coast. Animal Biodiversity and Conservation, 44.2: 219–227, Doi: https://doi. org/10.32800/abc.2021.44.0219 Abstract Natural hybridization between immigrant narrow–barred Spanish mackerel Scomberomorus commerson (Lacepède, 1800) and endemic West African Spanish mackerel Scomberomorus tritor (Cuvier, 1832) in the Egyptian Mediterranean coast. Immigrant narrow–barred Spanish mackerel, West African Spanish mackerel and specimens with an external appearance somewhere between these putative parents were collected from Abu Qir Bay, East Alexandria, Egypt. The hybrid index results and univariate and multivariate analysis indicated a natural hybridization between these two species. The discriminant function analysis successfully classified individual fish in the data to one of the three fish groups. Squared Mahalanobis distances extracted from the groups indicated the three groups were clearly distinct from each other. Moreover, distances between the hybrid and Scomberomorus tritor were longer than those of the hybrid and S. commerson. The mean values of the condition factor for the hybrid were significantly higher than those of S. commerson. Natural mortality of the hybrid was significantly lower than that of the exotic parent (S. commerson), indicating that the environmental conditions in the examined region are more suitable for the hybrid type species than for the invasive parental species. Key words: Immigrant, Scomberomorus commerson, Native Scomberomorus tritor, Natural hybridization, Egyptian Mediterranean coast Resumen Hibridación natural entre la carita estriada del Pacífico Scomberomorus commerson (Lacepède, 1800) y la carita oeste–africana Scomberomorus tritor (Cuvier, 1832) en la costa mediterránea egipcia. Se capturaron ejemplares inmigrantes de carita estriada del Pacífico y de carita oeste–africana y otros ejemplares con un aspecto externo intermedio entre estos progenitores putativos en la bahía de Abu Qir, al este de Alejandría, en Egipto. Los re- sultados del análisis univariado y multivariado del índice de hibridación indicaron que existía hibridación natural entre las especies parentales previstas. La función discriminante permite determinar si un determinado ejemplar del que se tienen datos pertenece a uno de los tres grupos y calcular su tasa de éxito. Las distancias cuadradas de Mahalanobis obtenidas entre los grupos analizados indicaron que los tres grupos estaban claramente dife- renciados y que las distancias entre los híbridos y Scomberomorus tritor eran superiores a las de los híbridos y S. commerson. Los valores medios del factor de condición de los ejemplares híbridos fueron significativamente mayores que los de S. commerson; además, la mortalidad natural de los híbridos fue significativamente inferior a la de los progenitores exóticos (S. commerson), lo que indica que las condiciones ambientales de la región estudiada son más adecuadas para el tipo híbrido que para las especies parentales invasoras. Palabras clave: Inmigrante, Scomberomorus commerson, Scomberomorus tritor autóctono, Hibridación natural, Costa mediterránea de Egipto Received: 19 III 21; Conditional acceptance: 31 V 21; Final acceptance: 22 VI 21 Shnoudy A. Bakhoum, National Institute of Oceanography and Fisheries, Alexandria, Egypt. Corresponding author: S. A. Bakhoum. E–mail: shnoudybakhoum@yahoo.com ORCID ID: 0000-0003-4691-9218 ISSN: 1578–665 X © [2021] Copyright belongs to the authors, who license the eISSN: 2014–928 X journal Animal Biodiversity and Conservation to publish the paper under a Creative Commons Attribution 4.0 License.
220 Bakhoum Introduction were taken to the nearest mm) and eight meristic counts. To minimize any variation resulting from allo- The Suez Canal was opened in 1869, connecting the metric growth, all morphometric measurements were Red Sea to the Mediterranean and allowing numerous standardized according to Reist (1985): Indo–Pacific species to invade the Mediterranean (Golani, 1998). This process of immigration through X'i,j = log Xi – b . (log TLj – log TLi) the Canal increased alien species of Indo–Pacific origin from 12 species in 1882 to 92 in 2010 (Keller where X'i,j is the standardized measurement of the i 1882; Zenetos et al., 2010). morphometric character; log Xi is the mean logarithm In 1985, Ben–Tuvia recorded that the narrow–barred of i morphometric character measurement; TLj is the Spanish mackerel S. commerson (Lacepède, 1800) had total length of the individual j; log TL is the logarithm reached the eastern part of the Mediterranean Sea. of the mean total length of pooled individuals and b Golani et al. (2002) later reported that this Lessepsian is the slope of the log X against logTL plot. migrant has expanded its distribution to the Aegean Sea. To elucidate the differentiation of the species and Several migrant Lessepsian fishes are now well– expected hybrid we used forward stepwise discrimi- established in the eastern Mediterranean. Halim and nant analysis (DA) on the characters, based on the Rizkalla (2011) published a checklist of 42 immigrant generalized Mahalanobis distance to determine the Erythrean fish in the Egyptian Mediterranean, 17 of similarity between groups and the ability of these which are commercially exploited. variables to identify the specimens correctly (Hair et Permanent change of habitat has a great effect al., 1998). We used univariate analysis of variance on the biometric characters of aquatic organisms (one way ANOVA) for meristic and size–adjusted (Abd El–Gawad et al., 1995; Bakhoum, 2017). In the data sets and multivariate discriminant function Egyptian Mediterranean waters, the immigrant Brush– analysis to select the important variables (Henault tooth lizardfish showed a sufficiently high degree of and Fortin, 1989). biometric differences to recognize the Mediterranean The hybrid index was calculated according to brush–tooth lizardfish (Saurida undosquamis) as a Witkowski and Blachuta (1980): distinct group from that of the Red Sea Fish (Bak- houm, 2000). Hybrid index = H – M1 / M2 – M1 Hybridization is defined as the crossing of geneti- cally distinguishable groups or individuals. It includes where, M1 is the numerical value of the same cha- crosses both between lineages of the same species racter of S. tritor, M2 the numerical value of a cha- (intraspecific) and between individuals of different racter of S. commerson, and H the numerical value species (Pinheiro et al., 2019). of hybrid characters. The invasion of closely related fish species may Characters of the hybrid approach 50 are interme- disturb a habitat and lead to an increasing incidence of diate, while characters close to 0 or 100 indicate a interspecific hybridization. It may also facilitate hybrid character state close to that of a parent species. The zones where the likelihood for interbreeding between commonly used length–weight relationship was applied: native and exotic species is seriously increased (Cos- tedoat et al., 2005; Almodóvar et al., 2012). W = a . L. b The aim of the present study was to detect hybrids between the native species West African Spanish where L is total length (cm), W is weight (g), and a mackerel S. tritor (Cuvier, 1832) and the exotic species and b are constants. S. commerson (Lacepède, 1800 ), and to evaluate the The coefficient of condition (Fulton condition factor, degree of hybrid adaptation in Egyptian Mediterranean K) was calculated from the equation: waters east of Alexandria. K = 100 . W / L3 Material and methods where W is the gutted weight in grams, L the total length in cm. This factor is often used as an approximation Study area even when the allometric factor is theoretically more appropriate (Bagenal and Braum, 1971; Ricker 1975). Between November 2019 and January 2020, 102 spe- The natural mortality coefficient 'M' was calculated cimens (27 S. tritor, 33 S. commerson and 42 possible by the method described by Ursin (1967). Data of hybrid fishes) were collected with the help of local condition factor and natural mortality were statistically fishermen using daytime purse seine fishing gear from analyzed using ANOVA. Abu Qir Bay in the Egyptian Mediterranean coast, All statistical analyses were performed using the east of Alexandria (latitude from 30º 5' to 30º 20' N SPSS PC ver. 16 software packages. and longitude from 31º 15' to 31º 25' E). Methods Results The biometric characters examined included twenty– Comparing morphological features of the parental one morphometric measurements (all measurements species with expected hybrid showed that the back
Animal Biodiversity and Conservation 44.2 (2021) 221 A B C Fig. 1. Photographs of parent species and putative hybrids: A, Scomberomorus commerson; B, Scomberomorus tritor; C, Hybrid form. Fig. 1. Fotografías de las especies parentales y los híbridos putativos: A, Scomberomorus commerson; B, Scomberomorus tritor; C, Hybrid form. colour of S. tritor was bluish–green. Sides were distinct from both in other characters. In contrast, the silvery, with about three rows of vertical elongated hybrid index revealed that hybrid specimens contained spots and lateral line gradually curving down towards 4 individual characters with a hybrid index > 100 and the caudal peduncle. Conversely, the back of S. < 0, 2 intermediate characters (hybrid index 45–55), commerson was iridescent blue–green, and sides 3 close to S. commerson (hybrid index > 55) and 19 were silver, with numerous wavy vertical bands. The close to S. tritor (hybrid index < 45) (see table 1). lateral line abruptly bent downward below the end of a second dorsal fin. Biometric characters The hybrid back was blue–green and its sides con- tained vertical elongated spots and numerous wavy Table 1 summarizes a comparison of 21 morphometric vertical bands inherited from both parental species. measurements and eight meristic counts between Moreover, the lateral line gradually curved downwards parent species and hybrid groups. below the end of the second dorsal fin (fig. 1). Univariate analyses The hybrid index One–way ANOVA indicated significant differences of meristic counts and morphometric measurements For some characters, the average values of hybrids (p < 0.001) between the hybrid groups and parental were close to either S. commerson or S. tritor but species. Tukey's honest–significant difference (HSD) of
222 Bakhoum Table 1. Hybrid index of meristic and morphometric measurements (mean ± SD) of Scomberomorus tritor, Scomberomorus commerson and hybrid specimens collected from Abu Qir Bay coast, east off Alexandria, Egypt: Hi, hybrid index. Tabla 1. Índice de hibridación de las mediciones merísticas y morfométricas (media ± DE de los ejemplares de Scomberomorus commerson y Scomberomorus tritor y los híbridos capturados en la bahía de Abu Qir, al este de Alejandría: Hi, índice de hibridación. S. tritor S. commerson Hybrid Hi Biometric characters First dorsal fin 15.78 ± 1.093 (15–18) 16.17 ± 0.983 (15–18) 15.86 ± 0.727 (14–17) 20.51 spines and rays Second dorsal fin 16.56 ± 0.882 (15–18) 16.67 ± 1.633 (15–19) 16.43 ± 0.676 (15–18) –118.18 spines and rays Anal fin spine 17.78 ± 1.302 (16–20) 17.67 ± 1.633 (16–20) 17.50 ± 1.044 (16–20) 254.55 and rays Pectoral fin spine 19.56 ± 1.509 (18–22) 22.17 ± 1.169 (21–24) 21.76 ± 1.338 (20–24) 84.29 and rays Ventral fin spine I±5 I±5 I±5 – and rays Dorsal finlets 8.56 ± 0.726 (7–9) 9.33 ± 0.516 (9–10) 9.62 ± 0.590 (8–10) 137.66 Anal finlets 8.89 ± 0.333 (8–9) 9.50 ± 0.548 (9–10) 9.52 ± 0.512 (9–10) 103.28 Vertebrae (total) 45.78 ± 0.667 43.00 ± 1.265 44.19 ± 1.436 57.19 (45–47) (42–45) (41–46) Morphometric measurement (mm) Total length 275.38 ± 44.201 394.17 ± 43.407 312.95 ± 56.743 31.63 (240–375) (310–430) (262–455) Forked length 248.63 ± 44.622 359.33 ± 50.162 275.10 ± 52.371 23.91 (215–350) (262–395) (233–410) Standard length 241.63 ± 42.671 349.83 ± 48.967 275.00 ± 50.838 30.84 (212–340) (264–392) (231–398) Predorsal length 62.75 ± 8.631 85.17 ± 10.610 67.76 ± 11.036 22.35 (55–80) (64–92) (51–97) Prepectoral length 58.63 ± 7.347 (51–72) 79.00 ± 10.621 (62–90) 65.29 ± 9.660 (56–91) 32.70 Preanal length 132.38 ± 16.370 194.83 ± 32.591 147.90 ± 26.760 24.85 (113–138) (145–225) (123–210) Prepelvic length 61.63 ± 6.948 (55–75) 88.67 ± 4.590 (83–95) 67.71 ± 10.340 (59–92) 22.49 Body depth 47.38 ± 7.671 (38–60) 64.67 ± 7.202 (60–73) 53.90 ± 7.409 (45–74) 37.71 Caudal peduncle length 17.88 ± 3.523 (15–25) 25.67 ± 3.724 (20–30) 21.57 ± 3.501 (18–30) 47.37 Caudal peduncle depth 10.50 ± 2.204 (9–14) 14.17 ± 1.602 (12–16) 11.19 ± 3.371 (8––13) 18.80 Dorsal rays height 24.25 ± 2.816 (21–28) 35.50 ± 7.007 (23–40) 27.81 ± 27.81 (24–40) 31.64 Anal base length 23.00 ± 5.732 (19–35) 36.17 ± 7.808 (22–44) 26.62 ± 5.220 (21–39) 27.49 Head length 56.38 ± 5.927 (52–69) 78.00 ± 12.000 (58–88) 63.48 ± 8.418 (55–86) 32.84 Head width 23.25 ± 3.655 (18–29) 32.33 ± 3.933 (26–36) 25.76 ± 4.122 (22–36) 27.64 Head depth 36.50 ± 4.811 (31–46) 49.00 ± 4.817 (42–54) 40.76 ± 4.959 (30–53) 34.08 Head depth passing through eyes 18.13 ± 2.850 (15–23) 30.83 ± 3.764 (25–35) 27.43 ± 4.261 (20–36) 73.23 Eye diameter 11.88 ± 0.835 (10–13) 16.00 ± 2.608 (12–19) 12.62 ± 1.564 (17–11) 17.96 Interorbital width 17.38 ± 1.996 (15–21) 24.17 ± 2.483 (20–27) 19.33 ± 3.055 (27–16) 28.72 Snout length 21.75 ± 2.188 (20–26) 31.67 ± 3.559 (26–35) 24.52 ± 3.710 (34–21) 27.92 Upper jaw length 32.50 ± 3.295 (29–39) 43.83 ± 3.251 (39–47) 35.76 ± 4.493 (48–30) 28.77 Lower jaw length 31.88 ± 3.227 (29–39) 45.00 ± 3.225 (39–48) 37.86 ± 4.607 (34–49) 45.58
Animal Biodiversity and Conservation 44.2 (2021) 223 Table 2. Significant differences between S. tritor (St), S. commerson (Sc) and hybrid (H) specimens based on ANOVA followed by the Tukey HSD test (honestly significant difference). (Significance level * p < 0.05, ** p < 0.01). Tabla 2. Diferencias significativas entre los ejemplares de S. tritor (St), S. commerson (Sc) y los híbridos (H) basadas en el ANOVA y el test HSD de Tukey (diferencia honestamente significativa). (Nivel de significación * p < 0,05; ** p < 0,01)". Tukey HSD test F–value St vs. Sc St vs. H Sc vs. H Biometric characters First dorsal fin spines and rays 56.723** 0.000** 0.891 0.000** Second dorsal fin spines and rays 4.158* 0.091 0.758 0.018* Anal fin spine and rays 1.634 0.203 0.933 0.313 Pectoral fin spine and rays 18.37** 0.000** 0.000** 0.683 Dorsal fin lets 21.742** 0.000** 0.000** 0.855 Anal fin lets 13.401** 0.001** 0.000** 0.990 Vertebrae (total) 64.642** 0.000** 0.000** 0.000** Morphometric measurement (mm) Total length 20.126** 0.000** 0.100 0.000** Forked length 7.137** 0.003** 0.015* 0.549 Standard length 19.874** 0.000** 0.000** 0.220 Predorsal length 0.084 1.000 0.934 0.941 Prepectoral length 0.658 0.665 0.529 0.996 Preanal length 45.093** 0.000** 0.000** 0.186 Prepelvic length 24.289** 0.000** 0.001** 0.001** Body depth 46.902** 0.000** 0.000** 0.892 Caudal peduncle length 43.119** 0.000** 0.000** 1.000 Caudal peduncle depth 5.052** 0.010** 0.700 0.041* Dorsal rays height 11.288** 0.000** 0.001** 0.714 Anal base length 10.572** 0.007** 0.000** 0.769 Head length 4.776* 0.025* 0.031* 0.891 Head width 7.850* 0.008** 0.002** 1.000 Head depth 3.115 0.065 0.123 0.803 Head depth passing through eyes 87.776** 0.000** 0.000** 0.089 Eye diameter 12.91** 0.003** 0.000** 0.711 Interorbital width 25.627** 0.000** 0.000** 0.483 Snout length 28.661** 0.000** 0.000** 0.385 Upper jaw length 0.922 0.947 0.400 0.666 Lower jaw length 37.766** 0.000** 0.000** 0.869 meristic counts indicated that the significant differences species. The hybrid type differed in 15 and 3 measu- between parental species were found in five charac- rements from S. tritor, and S. commerson, respectively ters. The differences between hybrid and S. tritor were (table 2). observed in four meristic counts, while hybrid type varied from S. commerson only in first and second Multivariate analysis dorsal fin spines and rays and vertebrae (p < 0.001). Canonical variate analysis (CVA) was performed on Adjusted morphometric measurements revealed meristic counts and twenty morphometric ratios to 17 of 21 significant characters between parental assess the shape variation between the two species
224 Bakhoum Table 3. Discriminant analysis classification Table 4. Discriminant analysis classification showing the percentage of specimens classified showing the percentage of specimens classified in each species, based on meristic counts: St, in each species, based on morphometric ratios: Scomberomorus tritor; Sc, Scomberomorus St, Scomberomorus tritor; Sc, Scomberomorus commerson; H, hibrid. commerson; H, hibrid. Tabla 3. Clasificación según el análisis Tabla 4. Clasificación según el análisis discriminante en la que se muestra el discriminante en la que se muestra el porcentaje porcentaje de ejemplares clasificados en cada de ejemplares clasificados en cada especie, especie, según los estudios merísticos: St, según las proporciones morfométricas: St, Scomberomorus tritor; Sc, Scomberomorus Scomberomorus tritor; Sc, Scomberomorus commerson; H, híbrido. commerson; H, híbrido. Predicted species Predicted species Species St Sc H Species St Sc H St 94.40 0.00 5.60 St 100.00 0.00 0.00 Sc 0.00 100.00 0.00 Sc 0.00 100.00 0.00 H 0.00 0.00 100.00 H 0.00 0.00 100.00 and hybrid form. Consequently, standardized ca- The mean values of condition factors of S. tritor nonical discriminant function coefficients extracted fish (0.803 ± 0.279) were higher than those of S. com- two meristic factors and seven morphometric ratios. merson (0.354 ± 0.193) and hybrid (0.660 ± 0.083) The discriminant function successfully identified the fish. Analysis of variance indicated significant differen- membership of individual fish in the data to one of ces in the mean values of condition factor between the three fish groups. The percentage of correctly parental species (F = 7.277, p < 0.01), S. tritor and identified specimens based on meristic counts for the hybrid fish (F = 61.921, p < 0.01) and between S. hybrid was 100 % and for S. tritor and S. commerson commerson and hybrid fish (F = 26.110, p < 0.01). individuals it was 94.4 % and 100 %, respectively (table 3). Identification of fish groups based on se- Natural mortality ven landmark morphometric ratios classified 100 % parental species and hybrid (table 4). The hybrid fish had the least mean value of natural CVA extracted two CVs, accounting for 100.00 % mortality coefficient (0.177 ± 0.024) followed by S. variations and showed three groups with no overlaps tritor (0.203 ± 0.015). S. commerson had the highest between groups, with a position of hybrid specimens mortality value (0.382 ± 0.126). Statistical analysis lying between expected parental species. Moreover, revealed significant differences in the natural mortality CVA plots suggested that hybrids were resultant due of S. commerson compared with S. tritor (F = 34.151, to crossing between S. tritor and S. commerson p < 0.01) and the hybrid (F = 46.011, p < 0.01). (fig. 2). Analysis of variance revealed no significant diffe- Squared Mahalanobis distances extracted among rence in the mean values of natural mortality between groups of S. tritor, S. commerson and hybrid speci- S. tritor and the hybrid (F = 2.020, p > .05). mens based on meristic and morphometric characters were highly significant (P < 0.0001), indicating that all groups were clearly distinct from each other, and Discussion squared Mahalanobis distances between hybrid and S. tritor were longer than those hybrid and S. commerson. Nature hybridization in most cases is a temporal phenomenon occurring at different scales over an Length–weight relationship and condition factor extended time frame (Avise and Walker, 2000). Hybrid species, especially those leading to genomic The relationship between total length (cm) and total introgression, may be an evolutionarily constructive weight (W) was represented by the equations: process, as occurred in the family Salmonidae (Ar- For S. tritor nold, 1997; Dowling and Secor, 1997). Extensive W = 0.0245 . L . 2.6548 (r2 = 0.9655) hybridization and introgression occurs more com- S. commerson monly in fish than in other vertebrates of comparable W = 0.0092 . L . 2.1036 (r2 = 0.9666) levels of genetic divergence (Epifanio and Nielsen, Hybrid form 2001). Almodóvar et al. (2012) recently described a W = 0.0192 . L . 2.3997 (r2 = 0.9455) case of natural hybridization between invasive bleak
Animal Biodiversity and Conservation 44.2 (2021) 225 A B 1 100 1 5.0 2 2 3 3 Centroid Centroid 50 2.5 Function 2 2 Function 2 1 2 1 0.0 0 3 3 –2.5 –50 –5.0 –100 –5.0 –2.5 0.0 2.5 5.0 –100 –50 0 50 100 Function 1 Function 1 Fig. 2. Plots of canonical variate analysis based on meristic counts (A) and morphometric ratios (B) for S. tritor (1), S. commerson (2) and putative hybrid (3) showing frequency of specimen distribution in respective group on the first two axes. Fig. 2. Gráficos del análisis de variables canónicas según los caracteres merísticos (A) y según las pro- porciones morfométricas (B) de S. tritor (1), S. commerson (2) y los híbridos putativos (3) en los que se muestra la frecuencia de la distribución de los ejemplares en el grupo respectivo en los dos primeros ejes. Alburnus alburnous and endemic calandino Squalius Many researchers use biometric characters to alburnoides complex following a short period of identify natural hybrids in fish (Reist et al., 1992; contact. This study deals with the characterization Bakhoum, 2009; Jacquemin and Pyron, 2016). In of the hybrids and their distinction and similarities the present study, the hybrid index revealed that with the parental species. most characters studied in hybrids were closer to Hybridization in nature is generally the result of either S. commerson or S. tritor, and one interme- interference by humans, through the construction of diate character revealed the hybrid nature of these reservoirs, for example, or introduction of exotic species, specimens. Canonical variate analysis (CVA) allowed or modification of rivers and Seas (Crivelli and Dupont, parent species to be distinguished from hybrids. No 1987; Pouyaud and Agnèse, 1995; Agnese et al., 1998; overlapping between groups was revealed, and clas- Bakhoum, 2019). The Suez Canal is an artificial water- sification in the respective group was 100 % correct. way connecting the tropical Red Sea and the subtropical CVA placed hybrids in a position between groups Eastern Mediterranean Sea. This example of human of S. commerson and S. tritor, indicating that hybrids intervention caused a global change in the distribution were resultant from crossing between the two species. of native and non–native fishes in Mediterranean waters Squared Mahalanobis distances indicated that the hy- (Ben–Tuvia, 1985; Golani et al., 2002). brid form was relatively closer to S. commerson than Natural hybridization occurs when reproductive to S. tritor. This may attribute to the back–crossing barriers break down. These barriers may be phys- between the first generation of hybrid specimens with iological, behavioural or geographic. Hybridization parental S. tritor fish. between S. commerson and S. tritor in the Suez Canal The condition factor is used to compare condition, is an example. fitness or wellbeing of fish. It is based on the hypoth- Reproductive barriers between species, both esis that heavier fish of a particular length are in a pre– and post–zygotic, appear to be incomplete for better physiological condition (Bagenal and Tesch, many fishes (Simon and Noble, 1968; Rosenfield et 1978). It is strongly influenced by both biotic and abi- al., 2000; Hendry et al., 2000). The parental species otic environmental conditions and can be used as an examined have pelagic eggs and larvae (Collette, index to assess the status of the aquatic ecosystem 1986) and the spawning season of S. tritor from July to in which fish live (Anene, 2005). August interfered with the spawning of S. commerson, The mean values of condition factors of endemic which extends from October to July (Collette and Nauen, S. tritor fish were higher than those of immigrant S. 1983; Collette and Russo, 1984), thus providing great commerson and hybrid fishes due to their adaptation opportunity for crossbreeding. to environmental conditions over many years. The
226 Bakhoum mean values of the condition factor for the hybrid Sciences, 5: 43–47. were significantly higher than those of S. commerson, Arnold, M. L., 1997. Natural Hybridization and Evolu- possibly because exotic species are strongly influ- tion. Oxford University Press, New York. enced by both biotic and abiotic situations in the Arnold, M. L., Hodges, S.A., 1995. Are hybrids fit or new habitat. Moreover, recent studies have provided unfit relative to their parents? Trends in Ecology evidence for hybrid fitness when compared to parental and Evolution, 10: 67–71, Doi: 10.1016/S0169- species (Arnold and Hodges, 1995; Reyer, 2008). 5347(00)88979-X Natural mortality (M) is an essential parameter in Avise, J. C., Walker, D., 2000. Abandon all species determining fish stock and an indicator of the adaptation concepts? A response Conservation Genetics, 1: of a population of fish. IIes (1968) found that in any 77–80, Doi: 10.1023/A:1010189805191 fish population the mortality rate and the size at which Bagenal, T. B., Braum, E., 1971. Eggs and early life maturity is achieved determines the proportion capable history. In: Methods of Assessment of Fish pro- of reproduction and the relative reproductive potential. duction in fresh waters, IBP Handbook 3: 165–201 In the present study, the natural mortality of the hybrid (T. Bagenal, Ed.). Blackwell Scientific Publication, and S. tritor were significantly lower than that of the Oxford. exotic parent (S. commerson), indicating that the envi- Bagenal, T., Tesch, F. W., 1978. Age and Growth. In: ronmental conditions in the examined region are more Methods of Assessment of Fish Production in Fresh suitable for the hybrid type and native fishes than for Waters, IBP Handbook 3: 101–136 (T. Bagenal, invasive parental species. A comparison of the natural Ed.). Blackwell Scientific Publication, Oxford. mortality coefficient of S. undosquamis from the two Bakhoum, S. A., 2000. Comparative study on brush– habitats indicated that the natural mortality coefficient tooth lizardfish Saurida undosquamis (Richard- for the emigrant to Mediterranean fish was comparative- son), from the Red Sea and Mediterranean Sea ly higher than that of endemic Red Sea fish (Bakhoum, coasts of Egypt. Oebalia, International Journal of 2000). This may be attributed to variation in environ- Marine Biology and Oceanography, 26: 35–48. mental conditions. El–shenawy et al. (2006) recorded – 2009. Biometric characteristics and some biological that the range of water temperatures in the Egyptian features of natural hybrids between Nile tilapia Mediterranean coast was wide(17.14–26.31 ºC), with Oreochromis niloticus and blue tilapia Oreochromis narrow fluctuations in salinity (37.51–39.710 ‰). In aureus in Lake Edku, Egypt. International Journal contrast, in the Red Sea coastal waters, temperatures of Ichthyology, 15(4): 191–204. fluctuated between 20.8 ºC and 28.1 ºC and salinity – 2017. Shape and behavior of aquatic organisms. ranged between 39.0 ‰ and 40.40 ‰. Differences in LAP Lambert Academic publishing, Germany. temperature between habitats leads to varied natural – 2019. Fish Assemblages in Surf Zone of the Egyp- mortality values. The relationship between growth and tian Mediterranean Coast off Alexandria. Turkish natural mortality is strong, but growth rates depend on Journal of Fisheries and Aquatic Sciences, 19(4): temperature, explaining the effects of temperature on 351–362, Doi: 10.4194/1303-2712-v19_4_09 natural mortality (Gislason et al., 2010). Ben–Tuvia, A., 1985. The impact of the Lessepsian We hope this paper helps to promote scientific (Suez Canal) fish migration in the Eastern Med- research into the importance of natural hybridization iterranean ecosystem. In: Mediterranean Marine on living resource management issues. Ecosystem, NATO Conference Series, I Ecology, 8: 367–375 (A. Moraitou–Apostolopoulou, V. Kiortsis, Eds.). Springer, Boston, MA, Doi: 10.1007/978-1- References 4899-2248-9_17 Collette, B. B., 1986. Scombridae (including Thunni- Abd El–Gawad, A. M, Bakhoum, Sh. A., Ragheb. E., dae, Scomberomoridae, Gasterochismatidae and 1995. Comparison of meristic and morphometric Sardidae). In: Fishes of the north–eastern Atlantic characters of Solea aegyptiaca in Mediterranean and the Mediterranean, volume 2: 981–997 (P. Sea and Lake Qarun, Egypt. Bulletin of the Na- J. P. Whitehead, M. L. Bauchot, J. C. Hureau, J. tional Institute of Oceanography and Fisheries, Nielsen, E. Tortonese, Eds.). Unesco, Paris. ARE, 21: 451–459. Collette, B. B., Nauen, C. E., 1983. Scombrids of Agnese, J. F., Adepo–gourene, B., Pouyaud, L., the world. An annotated and illustrated catalogue 1998. Natural hybridization in tilapias. In: Genetics of tunas, mackerels, bonitos and related species and Aquaculture in Africa Collection colloques et known to date. FAO Fisheries Synopsis, 125(2): seminires: 95–103. ORSTOM, Paris. 137. Food and Agriculture Organization of the Almodóvar, A., Nicola, G. G., Leal, S., Torralva, M. , United Nations, Rome. Elvira, B., 2012. Natural hybridization with invasive Collette, B. B., Russo, J. L., 1984. Morphology, sys- bleak Alburnus alburnus threatens the survival of tematics, and biology of the Spanish mackerels Iberian endemic calandino Squalius alburnoides (Scomberomorus, Scombridae). Fishery Bulletin, complex and Southern Iberian chub Squalius 82: 545–692. pyrenaicus. Biological Invasions, 14: 2237–2242, Costedoat, C., Pech N., Salducci, M. D., 2005. Evo- Doi: 10.1007/s10530-012-0241-x lution of mosaic hybrid zone between invasive and Anene, A., 2005 Condition factors of four cichlid spe- endemic species of Cyprinidae through space and cies of a man–made lake in Imo state, Southeast, time. Biological Journal of the Linnean Society, 85: Nigeria. Turkish Journal of Fisheries and Aquatic 135–155. Doi: 10.1111/j.1095-8312.2005.00478.x
Animal Biodiversity and Conservation 44.2 (2021) 227 Crivelli, A. J., Dupont, F., 1987. Biometrical and biolog- Schweizerischen Gesellschaft für die gesamten ical features of Alburnus alburnus X Rutilus rubilio naturwissenschaften, 28(3): 1–28. natural hybrids from Lake Mikri Prespa, northern Pinheiro, A. P. B., Melo, R. M. C., Teixeira, D. F., Greece. Journal of Fish Biology, 31: 721–733. Doi: Birindelli, J. L. O., Carvalho, D. C., Rizzo, E., 2019. 10.1111/j.1095-8649.1987.tb05275.x ntegrative approach detects natural hybridization Dowling, T. E., Secor, C. L., 1997. The role of hybrid- of sympatric lambaris species and emergence of ization and introgression in the diversification of infertile hybrids. Scientific Reports, 9: 1–11, Doi: animals. Annual Review of Ecology, Evolution, and 10.1038/s41598-019-408 Systematics, 28: 593–619, Doi: 10.1146/annurev. Pouyaud, L., Agnese, G. F., 1995. Phylogenetic re- ecolsys.28.1.593 lationships between 21 species of three tilapiine El–shenawy, M., Farag, A., Zaky, M., 2006. Sanitary genera Tilapia, Sarotherodon and Oreochromis and aesthetic quality of Egyptian coastal Waters using allozyme data. Journal of Fish Biology, 47: of Aqaba Gulf, Suez Gulf and Red Sea. Egyptian 26–38, Doi: 10.1111/j.1095-8649.1995.tb01870.x Journal of Aquatic Research. 32: 120–234. Reist, J. D., 1985. An empirical evaluation of several Epifanio, J., Nielsen, J., 2001. The role of hybridization univariate methods that adjust for size variation in in the distribution, conservation and management morphometric data. Canadian Journal of Zoology, of aquatic species. Reviews in Fish Biology and 63(6): 1429–1439. Fisheries, 10: 245–251. Reist, J. D., Vuorinen, J., Bodaly, R. A., 1992. Ge- Gislason, H., Rice, J., Niels, D., Pope, J. G., 2010. netic and Morphological identification of coregonid Size, growth, temperature and the natural mortality hybrid fishes from arctic Canada. Polish Archives of marine fish. Fish and Fisheries, 11: 149–158. of Hydrobiology, 39(3–4): 551–56. Golani, D., 1998. Impact of Red Sea fish migrants Reyer, H. U., 2008. Mating with the wrong species through the Suez Canal on the aquatic environ- can be right. Trends in Ecology and Evolution, ment of the eastern Mediterranean. Bulletin of Yale 23: 289–292. School of Forestry and Environmental Studies, Ricker, W. E., 1975. Computation and interpretation of 103: 375–387. biology statistics for fish population. Bulletin of the Golani, D., Orsi–Relini, L., Massuti, E., Quignard, Fisheries Research Board of Canada, Bulletin 191. J. P., 2002. CIESM Atlas of exotic species in the ARLIS, Alaska Resources Library and lnformation Mediterranean, vol 1. In: Fishes: pp?? (F. Briand, Services, Ottawa. Ed.). CIESM publishers, Monaco. Rosenfield, J. A., Todd, T., Greil, R., 2000. Asymmetric Hair, J., Anderson, R. E., Tatham, R. L., Black, W. hybridization and introgression between pink and C., 1998. Multivariate data analysis, 4th edition. chinook salmon in the Laurentian Great Lakes. Prentice Hall, Englewood Cliffs, NJ. Transactions of the American Fisheries Society, Halim, Y., Rizkalla, S., 2011. Aliens in Egyptian Me- 129: 670–679. diterranean waters. A check–list of Erythrean fish Simon, R. C., Noble, R. E., 1968. Hybridization in with new records. Mediterranean Marine Science, Oncorhynchus (salmonidea). I. Viability and in- 12(2): 479–490. heritance in artificial crosses of chum and pink Henault, M., Fortin, R., 1989. Comparison of meristic salmon. Transactions of the American Fisheries and Morphometric characters among spring–and Society, 97: 109–118. fall–spawning ecotype of Cisco (Coregonus artedii) Ursin, E., 1967. A mathematical model of some in southern Quebec. Canadian Journal of Fisheries aspects of fish growth respiration and mortality. and Aquatic Science, 46: 166–173. Journal of the Fisheries Research Board of Ca- Hendry, A. P., Vamosi, S. M., Latham, S. J., Hei- nada, 24(2): 2355–2453. buth, J. C., Day, T., 2000. Questioning species Witkowski, A., Blachuta, J., 1980. Natural hybrids realities. Conservation Genetics, 1: 67–76, Doi: Alburnus alburnus (L.) x Leuciscus cephalus (L.) 10.1023/A:1010133721121 and Rutilus rutilus (L.) x Abramis brama (L.) from IIes, T. D., 1968. Dwarfing or strutting in the genus the Rivers San and Biebrza. Acta Hydrobiologica, Tilapia (Cichlidae). Possibly recruitment mecha- 22: 473–487. nism. FAO Fisheries Report, Roma. Zenetos, A., Gofas, S., Verlaque, M., Cinar, M. Jacquemin, S. J., Pyron, M., 2016. A century of E., Bianchi, C. N., 2010. Alien species in the morphological variation in Cyprinidae fishes. BMC Mediterranean Sea by 2010. A contribution to the Ecology, 16: 48, Doi: 10.1186/s12898-016-0104-x application of European Union’s Marine Strategy Keller, C., 1882. Die fauna in Suez Canal und die Framework Directive. Part I. Spatial Distribution. diffusion der Mediterranean und Erythraischen Mediterranean Marine Science, 11(2): 381–493, Tierwelt. Neue Denkschriften der allgemeinen Doi: 10.12681/mms.87
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