GENETIC DIVERGENCE OF RABBITFISH SPECIES IN EGYPT USING ISSR-MARKERS
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J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 GENETIC DIVERGENCE OF RABBITFISH SPECIES IN EGYPT USING ISSR- MARKERS By Omaima E. Khafagy From Department of fish Resources and Aquaculture, Faculty of Environmental Agricultural Sciences, Suez Canal University. ABSTRACT Genus Siganus is represented in Egypt by two species, Siganus rivulatus and Siganus luridus. This study were, to studied the pattern of genetic variation in Siganus species in several localities of Egypt including Red Sea , Alexandria and Arish, to expose the potential of these markers in genetic studies requiring the detection of low polymorphism; as well as using ISSR- PCR DNA markers. Restriction endonucleases of the genomic DNA have been used to detect the genetic variability among and within fish populations. The relative from, molecular weight (MW) and band frequency fingerprints generated by the 6 primers revealed unique for each Siganus species in terms of number and position of ISSR bands. The wide distribution of microsatellites in Siganus species enables the analysis of inter-simple-sequence repeat (ISSR) markers. Very little of the variation was attributed to the locality and most of the variance appeared within localities. The variance components were significant (P
50 (family Siganidae, genus Siganus) that comprises 27 marine species divided in two subgenera, Siganus and Lo (Kuiter and Debelius, 2001). Different techniques have been applied to study genetic differentiation in two rabbitfish species (Siganus rivulatus and Siganus luridus), but to date not enough ISSR studies have been published on this species Siganids (rabbitfish) are a relatively small family of algaevorous fish widely distributed in the Indo-West Pacific Region (Woodland, 1983). Since the opening of the Suez Canal in the 19th century, a growing number of teleosts species have become permanently established in the Mediterranean Sea. As environmental parameters in the Mediterranean Sea are very different from those in the Red Sea, there is an opportunity to evaluate the gene flow associated with the acclimatization of these species to their new environment. Initial colonization may have been restricted to individuals with marginal genotypes compared to populations of the Red Sea, eventually better adapted to the Mediterranean Sea environment (Papaconstantinou, 1990). According to Ben-Tuvia (1978), the two main factors influencing the distribution of organisms over large zoogeographical areas are temperature and salinity that are notably different in both seas. Dominant currents in the Suez Canal are also an important factor favouring the Lessepsian migration. Since the opening of the Suez Canal, the number of migrant species into the eastern Mediterranean Sea continuously increased (Galil, 2000). Choosing an effective method to assess genetic variability in a group of individuals is of great interest to many researchers studying population genetics. In recent years, different molecular markers based on PCR amplification have been developed and rapidly have become essential tools in this field. Some of these markers are microsatellite-based, such as the inter-simple sequence repeat (ISSR) markers (Zietkiewicz et al., 1994). ISSR markers are generated from nucleotide sequences located between two microsatellite priming sites inversely oriented on opposite DNA strands and near enough to be amplified by PCR. This technique relies on the high polymorphism and wide distribution of microsatellites to detect low differentiation levels. The aim of this investigation was to assess genetic differentiation in samples localities distributed in Red Sea and Mediterranean Sea to expose the potential of these markers in genetic studies requiring the detection of low polymorphism and as a source of sequences for developing microsatellite markers. Research using ISSR markers has focused on evaluating genetic variation in terrestrial ecosystems. Less attention has been paid to the application of these markers in marine populations, where they have been used to evaluate the gene flow of two teleost species between the Red Sea and the Mediterranean Sea (Hassan et al., 2003). Using different molecular genetic techniques (mitochondrial DNA, Exon-Primed Intron-Crossing PCR amplification (EPIC) and Inter Simple Sequence Repeats (ISSRs), patterns of genetic differentiation on both sides of the Suez isthmus were tested on two Lessepsian rabbitfish species (Siganus rivulatus and Siganus luridus). In recent years, much of the research efforts have been focused in identifying the factors that allow successful invasions, with the promising goal to predict the identity of future invaders and vulnerable ecosystems (Goodwin et al., 1999 and Alcaraz et al., 2005). More than 59 Lessepsian fish species were recorded in the Levant basin. Golani, (1999) supposes that the existence of unsaturated niches in the eastern Levant basin, makes it more vulnerable to colonization. The environmental conditions in the new habitat and the characteristics of invaders play a prominent role in determining the success or failure of invasions (Reichard and Hamilton 1997). Such delay between the initial establishment of colonist and subsequent expansion is a common feature of biological invasion (Lee, 2002 and Rilov et al., 2004) and can be explained as an evolutionary phenomenon: the time needed for genetic adaptation to the 50
J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 new environment (Sakai et al., 2001). As a matter of fact, large scale changes in the distribution pattern of fish species may reflect changes in the oceanographic climatic conditions (Stephens et al., 1988) and recently many displacements of tropical affinity species in the Mediterranean Sea have been related to environmental changes (Guidetti and Boero 2001). MATERIALS AND METHODS Sample Collection and DNA Extraction The analysis of ISSR markers was performed on 60 S.rivulatus and S.luridus individuals were obtained from Mediterranean Sea (Alexandria and Arish) and Red Sea. DNA was extracted as described by Winnepenninck et al.,(1993). Samples stored in ethanol were rehydrated in PBS (0.137 M NaCl, 2.68 mM KCl, 10.1 mM Na2HPO4, 1.76 mM KH2PO4) and distilled water before DNA extraction. PCR amplification and sequencing Each PCR reaction of ISSR markers had a final volume of 25 µl, containing 20 ng of DNA template, 1×PCR buffer (16 mM (NH4)2SO4; 67 mM Tris-HCl, pH 8.8; 0.1%Tween-20), 1µM primer, 0.2 mM each dNTP, 5.2 mM Mg2Cl, and 0.75 U Taq DNA polymerase (Bioline). Amplifications were performed using a Touchdown PCR according to (Don et al., 1991) in a PTC-100 thermal cycles under the following conditions: 94°C 20 S min, 66°C 30 S , 72°C 2 min, and the annealing temperature was dropped 1°C for each of the subsequent 10 cycles followed by 30 cycles at 94°C 20 s, 55°C 30 s, and 72°C 2 min, with a final extension at 72°C 5 min (Fisher et al., 1996). Six primer ISSR (GATC(TCTG), HVH(TTCG)4, KRV(CT) 6, GATC(TCTG)7, YG(CT)9, YG(CA)9 (Table.1). Microsatellite fragment were amplified with the following conditions: 94°C 2 min, followed by 30 cycles of 92°C 1 min, Ta 1 min, and 72°C 30 S with a final extension step at 72°C 10 min. PCR reactions were carried out in a total volume of 25µl consisting of 20 ng DNA template,1× Roche Taq PCR buffer (10mM Tris-HCl, pH 8.3; 50 mM KCl,0.2 µM each forward and reverse primers, 0.2 mM each dNTP, 1.5 mM Mg2Cl, and 0.75 U Taq DNA polymerase (Roche). Electrophoresis and Band Scoring Products obtained by DNA extraction and amplification of ISSR markers were observed on 1.5% agarose gels stained with ethidium bromide using the UVP Gelworks densitometry software, which quantifies DNA and assigns a fragment size to each band by scoring against a molecular weight marker (Roche 100 bp ladder) (Fig. 2). A negative control was added in each run to test for contamination. To choose scorable bands and ensure reproducibility, a group consisting of 10 samples of each locality was amplified and analyzed twice. Microsatellite markers were evaluated for consistent amplification and polymorphism using according to Panaro et al.,( 2000). RESULTS The results of microsatellite analysis of muscle protein clear that each of the examined species had its own characteristic pattern which could distinguish not only between the two species and also between the same species. And the hybrid has more of its protein pattern. According to the Rp index, the primer ISSR(YG(CT)9) is the most appropriate to differentiate individuals, and a 200 bp band obtained with the primer ISSR (GATC(TCTG)8) is the most useful to differentiate sampling localities (Table.1). 51
52 The results for the six primer pairs that yielded amplification products are shown in (Table.3). One proved to be monomorphic 0.7627, and another) generated too many nonspecific bands and was judged unacceptable for analysis. Two microsatellites (0.7717 and 0.8924) generated scorable and polymorphic products. Observed heterozygosities (Ho)at YG(CA)9,GATC(TCTG)8 and KRV(CT)6 respectively. Table.1 required a higher final annealing temperature, and as a result, only 6 step- down cycles were needed, and the annealing temperature was kept at 59°C for 36 cycles. Structure of ISSR markers and annealing of anchored primers. Analysis of molecular variance also revealed a higher structure level between Red Sea and Mediterranean Sea than within the Mediterranean Sea. However, structure in all cases was very low, with 10% of the variance being attributable to the structure between Red Sea and the Mediterranean Sea, and only 1.5%of the variance being attributable to the structure between Alexandria and Arish (Mediterranean Sea). We noticed that there are very little of the variation was attributed to the locality and most of the variance appeared within localities. The variance components were significant (P
J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 ISSR markers provides data that can be used to amplify single microsatellite loci. In previous studies, microsatellites have been isolated from genomic libraries, and then these sequences have been useful in natural populations (Astanei et al., 2005) or as a tool of parentage identification (Walker et al., 2005). The development of microsatellite markers is a long and expensive process, however, and so some researchers examine the applicability of markers from related species (Evans et al., 2001). This study was clearly related to genetic differentiation between species. Furthermore, few loci are available in rabbitfish - related species, hence the isolation and characterization of microsatellite markers from the sequences amplified by anchored primers represents a feasible alternative as described previously (Keiper et al., 2006 and Varela et al., 2007). This technique provided a fast and cost-effective analysis of polymorphism in a group of individuals, and at the same time, sequence data were gathered to perform more studies using single microsatellite loci. Our findings uncovered a slight but detectable lowering of the S.luridus genetic diversity in the (Red Sea). Invading population compared with the parental one (Mediterranean Sea). These results stressed the importance to encompass wide geographic samplings in this kind of studies, so far limited to the Mediterranean Sea. Data Analysis Samples were collected in one locality in the Red Sea and two localities in the Mediterranean Sea (Alxandria and Arish). The usefulness of ISSR markers, as fingerprinting of the banding pattern obtained with each primer, was evaluated using the Rp index of Prevost and Wilkinson (1999), who found a strong relationship between this index and the ability of a primer to differentiate between individuals. The Rp of a primer is Rp = Ib, where Ib (band informativeness) is equal to 1 - [ 2 × (0.5- p)], p being the proportion of individuals containing this band. This index could be helpful as a primer choice criterion to perform fingerprinting analyses in a particular species. The value of this index for each primer does depend on the number of individuals. For these values to be comparable among different studies, however, the groups considered must have similar levels of genetic diversity and the studies must apply the same analytical procedure. The conditions in the Mediterranean, particularly in its region, are very different than in the Red Sea, thus potentially resulting in strong selective pressure. These results were Agreement with Papaconstantinou, 1990 and Golani 1993a). Finally, 200 microsatellites were found in the sequences of 28 ISSR markers, and two polymorphic microsatellite markers were developed may be located in a mosaic hybrid zone (Bierne et al., 2003). Genetic diversity and structure among regions and populations haplotype diversity (hd) was found to be higher in Red Sea than in any Mediterranean Sea populations, as well as in the combined Mediterranean Sea samples. This result was agreement with (Diamant, 1989). Structure of ISSR markers and annealing of anchored primers in (Table.1) required a higher final annealing temperature, and as a result, only 6 step-down cycles were needed, and the annealing temperature was kept at 59°C for 36 cycles. Diagonal lines separate microsatellite priming sites inversely oriented on opposite DNA strands and near enough to be amplified by PCR (Zietkiewicz et al., 1994) (Fig.1). They concluded that the rabbitfish of Red sea were not significantly different from a pure Siganus rivulatus locality, suggesting a high introgression of alleles of S. rivulatus in these individuals. DNA diversity is maintained during the early invasions, thus avoiding suboptimal assortments of genotypes and preserving the needed genetic plasticity to adapt to the new habitat. 53
54 They used the protein electrophoresis to confirm the identity of the two species and their hybrids where there are few characters have been detected by morphological analysis. This information accorded with the idea that Lessepsian migration involves many individuals since its beginning and emphasized the need to explore the causes which trigger migration itself, as for instance changes in the oceanographic climatic conditions (Keiper et al. 2006). Table (1): ISSR markers in two rabbitfish species Primer a Size Bands (bp) b Rp index 5' – YG(CA)9-3' 650,525, 450,250 1.57 5' – GATC(TCTG)8-3' 750, 800,950,550,200 3.14 5' – HVH(TTCG)4-3' 975,900,1025,1400 2.76 5' – KRV(CT) 6 - 3' 1425,1090,1050,1300 3.14 5' – GATC(TCTG)7-3' 1200,1350,1450,1525 256 5' – YG(CT)9-3' 1700,1250,950,750,650 1.59 a H :A,T, or C ; V:C,G, or A ;Y: C or T; K:G or T; R:A or G b Rp : resolving power. Table (2): Number of microsatellites which found in 19 ISSR markers ISSR Primer a Repeat Motif b Size Accession no. YG(CA)9 (CA)9 (ATTT)5(TA)7 (TG)8 683 AJ938137 (AC)7 (CAAC)3(CAAT)11 (CA)(TG)8 345 AJ938136 (CA)9 (AT) 5 (TG)28 237 AJ938135 GATC(TCTG)8 (TCTG)6 (TCCG)4(ACAG)6 750 AJ938129 (TCTG)8(ACAG)4(ACAG)6 775 AJ938128 (TCTG)6 (ACAG)6 650 AJ938127 (TCTG)6 (TCCG)4(ACAG)6 425 AJ938126 GATC(CTG)7 (CGT)7 (GAC)9 720 AJ938125 (CTG)6 (ACG)6 600 AJ938124 (TCG)6 (ACG)27 457 AJ938123 YG(CT)9 (CT)9 (AG)7 715 AJ938117 (TTCT)24 (CT)6 (GA)6 (AG)6 (GA)8 550 AJ938116 (TCTG)6 (TCCG)4(ACAG)6 730 AJ938115 KRV(CT)6 (CT)6 (TTG)4(AG)6 650 AJ938111 (TCTG)6 (TCCG)4(ACAG)6 450 AJ938110 (TTCG)4 (ACGA)11 200 AJ938109 HVH(TTCG)4 (TTCG)4 (ACAG)9 650 AJ938101 (TTCG)7(ACAG)6 350 AJ938100 (TTCG)6 (AT)5(AACG)6 250 AJ938199 a Y = C/T, R=A/G, V=A/C/G, H=A/C/T, K= G/T b At least nucleotides randomly repeated twice or three times 54
J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 Table (3):Characterization of six microsatellite markers in two rabbitfish species Locus Comments Ho Accession no YG(CA)9 Polymorphic 0.8924 AJ938137 GATC(TCTG)8 Monomorphic 0.7627 AJ938129 GATC(CTG)7 Mosic _ AJ938125 YG(CT)9 Unscorable _ AJ938117 KRV(CT)6 Polymorphic 0.7717 AJ938111 HVH(TTCG) 4 Monomorphic _ AJ938101 Fig 1: Structure of ISSR markers and annealing of anchored primers. Diagonal lines separate microsatellite priming sites inversely oriented on opposite DNA strands and near enough to be amplified by PCR. Arrows indicate direction of DNA polymerization (5'-3'). N represents an anchoring Nucleotide. MW Marker A B C D E F G (bp) 2000 1425 1350 1050 1000 950 725 600 500 525 475 250 Fig 2: ISSR markers ,Anchored primers generated polymorphic banding patterns in rabbitfish species from three localities Alexandria , Arish, and Red Sea. Lane A ,B ,C represented S.rivulatus of Alexandria; Arish; and Red Sea respectively and D ,E,F, represented S. luridus of Alexandria; Arish; and Red Sea respectively. G negative control No DNA. MW : DNA Molecular weight marker (Roche). 55
56 CONCLUSION The analysis of the populations of two rabbitfish species allowed concluding that the rabbitfish species were extant in the Red Sea before the construction of the Suez Canal based on the genetic similarity between all possible pairs of these populations. The conditions in the Mediterranean Sea, particularly in its region, are very different than in the Red Sea, thus potentially resulting in strong selective pressure. These results were Agreement with Papaconstantinou, 1990 and Golani, 1993a). ACKNOWLEDGMENTS We would like to thank prof. Dr. Magdy T. Khalil Science Faculty, Ain shams University, for his continues help in reading the mainscript of the article . And Special thanks to the Genetic Engineering Center University Ain Shams.We wish to acknowledge all fish farmers in collection fish samples in this study. REFERENCES Alcaraz, C., Vila-Gispert, A. and García-Berthou, E. (2005): Profiling invasive fish species: the importance of phylogeny and human use. Divers. Distrib. 11, 289– 298. Astanei I,Gosling E, Wilson, J., and Powel,l. E.(2005): Genetic variability and phylogeography of the invasive zebra mussel, Dreissena polymorpha (Pallas). Mol Ecol 14:1655–1666. Bariche, M. (2002): Biologie et e´cologie de deux espe`ces lessepsiennes, S. rivulatus et Siganus luridus (Te´le´- oste´ens, Siganidae) sur les coˆtes du Liban. The`se Universite´ de la Me´diterrane´e, Spe´cialite´: Sciences de l’Environnement, Chimie et Sante´. 223 pp. Ben -Tuvia, A. (1978): Immigration of fishes through the Suez Canal. Fish. Bull. 76 (249 pp.). Benson, G .(1999): Tandem Repeats Finder (TRF) a program to analyze DNA sequences. Nucleic Acids Res 27:573–580. Bierne, N., Borsa, P., Daguin, C., Jollivet, D., Viard, F., Bonhomme, F., and David, P. (2003): Introgression patterns in the mosaic hybrid zone between Mytilus edulis and M. galloprovincialis. Mol Ecol 12:447–461. Diamant, A. (1989): Lessepsian migrants as hosts: a parasitological assessment of rabbitfish Siganus luridus and S.rivulatus (Siganidae) in their original and new zoogeographical regions. Environmental Quality and Ecosystem Stability- Environmental Quality. ISEEQS Pub., Jerusalem, pp. 187–194. Don, RH., Cox, PT., Wainwright, BJ., Baker, K., and Mattick, JS. (1991): Touchdown PCR to circumvent spurious priming during gene amplification. Nucleic Acids Res 19:4008. Evans, B., Conod, N., and Elliot, NG. (2001): Evaluation of microsatellite primer conservation in abalone. J Shell Res 20:1065–1070. Fisher, PJ., Gardner, RC., and Richardson, TE. (1996): Single locus microsatellites isolated using 50 anchored PCR. Nucleic Acids Res 24:4369 – 4371. Frankham, R. (2005): Resolving the genetic paradox in invasive species. Heredity 94, 385. 56
J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 Galil, B.S. (2000): A sea under siege-alien species in the Mediterranean. Biol. Invasions 2, 177– 186. Golani , D.(1990): Environmentally-induced meristic changes in Lessepsian fish migrants, a comparison of source and colonizing populations. Bull. Inst. Oce´anogr. (Monaco) Spe´cial Issue 7, 143– 152. Golani , D. (1993a): Trophic adaptation of Red Sea fishes to the eastern Mediterranean environment: review and new data. Isr. J. Zool. 39 (4), 391– 402. Golani , D. (1993b): The sandy shore of the Red Sea-launching pad for Lessepsian (Suez Canal) migrant fish colonizers of the eastern Mediterranean. J. Biogeogr. 20, 579–585. Golani, D. ( 1998): Impact of Red Sea fish migrants through the Suez Canal on the aquatic environment of the eastern Mediterranean, Yale School Forest. Environ. Stud. 103, 375–387. Golani, D. (1999): The Gulf of Suez ichthyofauna-assemblage pool for Lessepsian migration into the Mediterranean.Isr. J. Zool. 45, 79– 90. Golani, D., Orsi-Relini, L., Massuti, E and Quignard, J.-P.(2004): Dynamics of fish invasions in the Mediterranean: update of the CIESM fish atlas. Rapp. Comm. Int. Mer. Médit.37, 367. Goodwin, B.J., McAllister, A.J., and Fahrig, L. (1999): Predicting invasiveness of plant based on biological information. Conserv. Biol. 13, 122–126. Guidetti, P. and Boero, F. (2001): Occurrence of the Mediterranean parrotfish Sparisoma cretense (Perciformes: Scaridae) in southeastern Apulia (south-east Italy). J. Mar. Biol. Assoc. U.K. 81, 717–718. Hassan, M., Harmelin-Vivien, M. and Bonhomme, F. (2003): Lessepsian invasion without bottleneck: example of two rabbitfish species (Siganus rivulatus and Siganus luridus). J. Exp. Mar. Biol. Ecol.291, 219–232. Hassana Mohamad, Mireille Harmelin-Vivienb, and Francois-Bonhommea. (2003): Lessepsian invasion without bottleneck:example of two rabbitfish species (Siganus rivulatus and Siganus luridus). Journal of Experimental Marine Biology and Ecology.291 , 219– 232. Holland, B.S. (2000): Genetics of marine bioinvasions. Hydrobiologia 420, 63– 71. Keiper, FJ., Hayden, MJ., and Wallwork, H. (2006): Development of sequence tagged microsatellites (STMs) for the barley scald pathogen Rhynchosporium secalis. Mol Ecol Notes 6:543–546. Kuiter, R.H and Debelius, H. (2001): Surgeonfishes, Rabbitfishes, and Their Relatives: A Comprehensive Guide to Acanthuroidei. TMC Publishing, Chorleywood, Herts, United Kingdom. 208 pp.Lee, C.E.(2002): Evolutionary genetics of invasive species. Trends Ecol. Evol. 17 (8), 386–391. Panaro, NJ., Yuen, PK., Sakazume, T., Fortina, P., Kricka, LJ and Widing P. (2000): Evaluation of DNA fragment sizing and quantification by the Agilent 2100 Bioanalyzer. Clin Chem 46:1851–1853. Papaconstantinou,C. (1990): The spreading of Lessepsian fish migrant into the Aegean sea (Greece). Sci. Mar. 54(4), 313– 316. 57
58 Por, F.D. (1978): Lessepsian migration: the influx of Red Sea biota into the Mediterranean by the way of the Suez Canal. Ecological Studies, vol. 23. Springer, Berlin. 228 pp. Prevost, A and Wilkinson, MJ. (1999): A new system of comparing PCR primers applied to ISSR fingerprinting to potato cultivars. Theor Appl Genet 98:107–112. Reichard, S.H and Hamilton, C.W. (1997): Predicting invasions of woody plants introduced into North America.Conserv. Biol. 11, 193– 203. Rilov, G., Benayahu, Y and Gasith, A. (2004): Prolonged lag in population outbreak of an invasive mussel: a shifting-habitat model. Biol. Inv.6, 34 –364. Sakai, A.K., Allendorf, F.W., Holt, J.S., Lodge, D.M., Molofsky, J., With, K.A., Baughman, S., Cabin, R.J., Cohen, J.E.,Ellstrand, N.C., McCauley, D.E., O'Neil, P., Parker, I.M., Thompson, J.N and Weller, S.G. (2001): The population biology of invasive species. Ann. Rev. Ecolog. Syst. 32,305–332. Stephens, J.S., Hose, J.H. and Love, M.S. (1988): Fish assemblages as indicators of environmental change in nearshore environments. In: Soule, D.F., Kleppel, G.S. (Eds.), Marine Organisms as Indicators. Springer-Verlag, New York, pp. 91– 105. Tsutsui, N.D., Suarez, A.V., Holway, D.A and Case, T.J. (2000): Reduced genetic variation and the success of an invasive species. Proc. Natl.Acad. Sci. U. S. A. 97, 5948–5953. Varela, MA., Gonza´lez-Tizo´n, A., Francisco-Candeira, M and Martı´nez-Lage, A. (2007): Isolation and characterization of polymorphic microsatellite loci in the razor clam Ensis siliqua. Mol Ecol Notes 7:221–222. Walker, D., Power, A,J and Avise, JC. (2005): Sex-linked markers facilitate genetic parentage analyses in knobbed whelk broods. J Hered 96:108–113. Winnepenninck, B., Backeljau, T., De and Wachter R. (1993): Extraction of high molecular weight DNA from molluscs. Trends Genet 9:407. Wonham, M.J., Carlton, J.T., Ruiz, G.M., and Smith, L.D. (2000): Fish and ships: relating dispersal frequency to success in biological invasions. Mar. Biol. 136, 1111– 1121. Woodland, D.J. (1983): Zoogeography of the Siganidae (Pisces).an interpretation of distribution and richness patterns. Bulletin of Marine Science, 33, 713–717. Woodland, D.J. (1990): Revision of the fish family Siganidae with descriptions of two new species and comments on distribution and biology. Indo-Pac. Fishes 19, 1–136. Zietkiewicz, E., Rafalski, A and Labuda, D. (1994): Genome fingerprinting by simple sequence repeat (SSR)-anchored polymerase chain reaction amplification. Genomics 20:176–183 58
J. Biol. Pham. Sci. Vol. 6, No. 1 July, 2008 دراسة االختالفات الوراثية ألسماك السيجان الموجودة فى مصر باستخدام تحليل ISSR-PCR أميمة خفاجى قسم الثروة السمكية -كلية العلوم الزراعية البيئية ـ جامعة قناة السويس تتمثل أسماك السيجان فـ مرـر والتـ تتبـ عائلـة Siganidaeبجـنس وادـه ـو Siganus ويوجه منها نوعان فقط ف مرر ما Siganus rivulatus :و Siganus luridus كان الههف من البحث و دراسة الفروق الوراثية واالختالفات بين المواق الثالث التـ أخـ ت منها العينات العريش اإلسكنهرية والبحر األدمر ،أثبتت الهراسة أن ناك اختالفات صغيرة لكل موقـ عل دهة وك لك ناك اختالفات عل مستوى الموق الواده . كانت ناك اختالفات وراثية عل مستوى الـ . DNAوباستخهام ادهث االختبارات والتحاليل الوراثية ISSRأمكن الكشف عن االختالفات الهقيقـة بـين كـل مجموعـة أو عشـيرة علـ دـهة وداخـل المجوعة نفسها .بل االختالفات داخل المواق نفسها.وبين المواق الت تم اختيار العينات منها. أمكن عن طريق المواق مقارنة الحزم المعزولة بالوزن الجزيئ و معرفة االختالفات الوراثية الهقيقة بين النوعين. كشف تحليل ISSRلعينات الـ DNAالمعزولة من البحر األدمـر والبحـر األبـيل المتوسـ ط (اإلسكنهرية ،العـريش عـن وجـود اختالفـات وراثيـة بنسـبة عاليـة بـين المواقـ الـثالث بينمـا كانـت االختالفات أقل داخل كل موق عل دهة ف العينات الت تمت دراستها. 59
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