Genetic Variations of Common Carp (Cyprinus carpio L.) In South-Eastern Part of Caspian Sea Using Five Microsatellite Loci

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World Journal of Zoology 6 (1): 56-60, 2011 ISSN 1817-3098 IDOSI Publications, 2011 Genetic Variations of Common Carp (Cyprinus carpio L.) In South-Eastern Part of Caspian Sea Using Five Microsatellite Loci Mehdi Yousefian Islamic Azad University, Qaemshahr Branch, Iran Abstract: Five highly variable microsatellite loci were used to investigate genetic variations and population structure of common carp of Caspian Sea. A total of 54 fish were genotyped giving 35 alleles over all loci. The mean number of alleles, per locus in population ranges from 5.5 to 13.0 and the mean observed heterozygosity at the five loci was 0.84. An analysis of genetic variations indicated the Ho within each groups varied between 0.412 to 1 which the lowest was in female at Loc5 loci and highest at Syp4 loci. The range of He was 0.696-0.856 that the lowest was in Lid II in male. Highly significant deviation from Hardy Weinberg, mostly due to deficits of heterozygote except for Ca3/4 and Z9/10 loci in male, based on 2-test, showed no deviation form HWE. Key words: Genetic variation Cyprinus carpio Microsatellite INTRODUCTION MATERIALS AND METHODS Common carp (Cyprinus carpio L.) is an important Fish Sample and DNA Isolation: A total of 54 adult economic species of fresh water fish, widely distributed as common carp (Cyprinus carpio L.) was sampled in culture fish In Iran. The wild common carp also are 2008-2009 from South Caspian Sea, Golestan present in Caspian Sea which people prefer the wild ones. province, Gomishan, Iran. Fins of live fish clipped This make the wild carps more expensive than the and immediately soaked in 95% ethanol while traveling culture ones, but due to over caught, the wild carp are and then stored at -20 C until DNA isolation. Total reduced in resources. For restocking millions of carp genomic DNA was extracted from ethanol-preserved fin fingerling are released to Caspian Sea by fishery tissues using traditional proteinase-k digestion and a organization (Shilat), every year. The wild carp for inland protocol of phenol-chloroform extraction with slight aquaculture is under investigation. Understanding the modifications [5]. genetic variations and genetic structure of Caspian common carp is important for protecting the genetic Amplification of Microsatellite Loci: Five pairs of resource, conservation gene hank and restraining the microsatellite primers designated for common carp, genetic decline. were used in this study. Polymerase chain reaction Extensively investigation by using different molecular (PCR) amplifications were performed in a 12.5 µl marker e.g. allozyme, RAPD and microsatellites were used volume containing 10-50 ng DNA, 1 PCR buffer [1-3]. Among different method introduced for genetic of (10 mmol/l tris Cl ph 8.3, 1.5 mmol/mgcl2, 50 mmol/l KCl), fish, Microsatellite technique seems to be the most 120 µmol/l dntps, 0.15 µmol/l primers and 0.5 U taqsuitable once. Microsatellite is variable nuclear genetic DNA polymerase. The reaction were performed by thermal markers, which are inherited co-dominantly in a mendelian cycle and the cycle were as follows: a pre-denaturation fashion. Microsatellites have been found suitable for a at 94 C for 5 min; followed by 30 cycles of denaturation variety of application in fisheries and aquaculture [4]. at 94 C for 0.5 min, annealing at proper temperature In the present study, polymorphic microsatellites (Table 1) for 40 s and elongation at 72 C for 40 s and a were applied to study genetic variations among common final elongation at 72 C for 10 min. PCR products carp population from Caspian Sea. Although suffering of were separated on 7.5% non-denaturing polyacrylamide over fishing and human impacts for many years in gels using TBE buffer in the gel and reservoirs at Caspian Sea, it is hope to preserve the gene bank of 200 V for 2 3 h according to alleles size, stained with valuable fishes of this unique lake of the word including ethidium bromide in water and visualized with common carp. ultraviolet. Corresponding Author: Mehdi Yousefian, Islamic Azad University, Qaemshahr Branch, Iran, E-mail: yousefianeco@yahoo.com. 56

Table 1: Characteristics of microsatellite markers in common carp Loci Primer sequence Annealing temperature C References Syp4 CACACCGGGCTACTGCAGAG GTGCAGTGCAGGCAGTTTGC 58 Crooijmans et al., 1997 Ca3/4 GGACAGTGAGGGACGCAGAC TCTAGCCCCCAAATT TTACGG 56 Dimsoski et al., 2000 Lidll ATCAGGTCAGGGGTGTCACG TGTTTATTTGGGGTCTGTGT 55 Turner et al., 2004 Z9/10 CGTCTGACAGCCTGCATG CTCGGCGCAGTAGGGAAC 56 Turner et al., 2004 Loc5 TTACACAGCCAAGACTATGT CAAGTGATTTTGCTTACTGC 58 Turner et al., 2004 Statistical Analysis: Indices of genetic diversity for alleles rang in size from 124 to 464 bp were found over the populations, e.g. The observed number of alleles (A), five loci. The number of allele ranged from 5 at LidII to 13 effective number of alleles frequency (Ne), allele at Ca3/4. The highest allelic frequency was 0.382 in female frequency (P), observed heterozygosity (Ho), expected spawners at Loc5 loci and 0.433 in male spawners at heterozygosity (He) [6], gene diversity, were calculated syp4 loci. and deviations from Hardy Weinberg Equilibrium (HWE) Genetic variations within population in experimental was estimated 2 test, Fst and Nm between populations group (male and female) for each locus were tested and were given by the software of GeneAlex. average observed hetrozygosity ranged from 0.412 to 1. The lowest observed genetic variation was in female at RESULTS Loc5 and highest at Syp4. Average expected hetrozygosity ranged from 0.696 to All five pair primer Syp4, Ca3/4, LidII, Lco5 and Z9/10 0.856, but the lowest was at LidII and highest at Z9/10 in related to microsatellite sites were applicable and males (Table 3). The exact test for fitness to Hardypolymorphic in wild common carp. These loci all were Weinberg equilibrium (HWE) on all loci indicated that, variable in population (Table 2). A total of 45 different Ca3-4 and Z9/10 in male were found to be in HWE Table 2: Allele frequencies at each locus in two sex groups locus Allele Female Male locus Allele Female Male Syp4 140 0.029 0.000 Ca3/4 220 0.059 0.067 156 0.324 0.433 232 0.000 0.067 160 0.118 0.000 244 0.029 0.133 164 0.059 0.067 248 0.206 0.133 168 0.265 0.133 252 0.176 0.000 172 0.000 0.133 260 0.088 0.200 184 0.088 0.000 268 0.000 0.400 188 0.029 0.000 292 0.059 0.000 192 0.088 0.067 296 0.206 0.367 196 0.000 0.167 304 0.059 0.000 Lidll 432 0.118 0.433 308 0.029 0.000 436 0.235 0.133 316 0.000 0.033 456 0.176 0.000 320 0.088 0.000 460 0.294 0.167 Z9/10 124 0.088 0.167 464 0.147 0.267 128 0.029 0.033 Loc5 200 0.000 0.000 132 0.265 0.100 236 0.059 0.067 136 0.088 0.067 240 0.088 0.133 140 0.265 0.267 244 0.029 0.133 144 0.059 0.067 260 0.118 0.000 152 0.059 0.067 284 0.147 0.200 160 0.088 0.100 288 0.382 0.400 164 0.059 0.100 300 0.176 0.000 168 0.000 0.033 57

Table 3: The expected (He) and observed heterozygosity (Ho)at five microsatellite loci of common carp Female brood N=17 Male brood N=15 ------------------------------------------------------ ----------------------------------------------------- Loci Ho He Ho He Syp4 1.000 0.791 1.000 0.740 LidII 1.000 0.791 0.867 0.696 Loc5 0.412 0.775 0.533 0.756 Ca3/4 0.882 0.856 0.933 0.769 Z9/10 0.941 0.825 0.867 0.856 Table 4: effective number of alleles (Ne) in five loci of common carp Female brood n=17 Male brood n=15 -------------------------------------------------------- ---------------------------------------------------- Loci Ne Na Ne Na Syp4 4.777 8.000 3.846 6.000 LidII 4.777 6.000 3.285 4.000 Loc5 4.446 7.000 4.091 6.000 Ca3/4 6.964 10.000 4.327 8.000 Z9/10 5.723 9.000 6.923 10.000 Table 5: The results of test of Hardy-Weinberg at different loci in common carp Female brood df Chi-square Prob. Sig. SYP4 28 58.212 0.001 *** LIDII 15 28.730 0.017 * LOC5 21 41.670 0.005 ** Ca3-4 45 82.668 0.001 *** Z9/10 36 57.716 0.012 * Male brood SYP4 15 45.000 0.000 *** LIDII 6 29.343 0.000 *** LOC5 15 37.500 0.001 ** Ca3-4 28 31.121 0.312 ns Z9/10 45 61.433 0.052 ns Table 6: The estimate Fst nd Nm between the loci Loci SYP4 LIDII LOC5 Ca3-4 Z9/10 Mean Nm 7.750 4.35 11.696 10.59 22.817 8.619 Fst 0.031 0.055 0.021 0.023 0.011 0.029 (P>0.01). The other loci significantly deviated from analysed by GeneAlex and the value was 0.794 shows the HWE (P<0.05) in male and female (Table 5). Another two groups of sex were distinct. characteristics for determining polymorphism of loci is the real and effective number of allele. The highest effective DISCUSSION allele in males and females were 6.923 and 6.96 and the lowest were 3.285 and 4.446, respectively. The highest real Recently, microsatellite were used for Dutch carp allele was in case of Ca3/4 and Z9/10 (Table 4). [1], French and Czech carp [2], Hungarian carp [3], In study of Population genetic differentiation, Chinese carp [8] and a few studies involved in Iranian gametal correlation coefficient (Fst), also known as common carp by protein electrophoresis [9] and coefficient of inbreeding and Gene flow (Nm) were PCR-RFLP molecular analysis [10]. The Caspian Sea computed to estimate the differences between is the most important habitat for native, common carp. populations. All Fst were larger than the standard with no Although over fishing has been a serious problem in genetic differentiation between two groups of male and Caspian Sea, yet there is a large scale stock releasing or female. resource enhancement for common carp in Caspian Sea in The average of Fst was (0.028) and the average of Nm Iran. For this unique stock of common carp, genetic between male and female was 8.619 (Table 6). The variation and population structures is little known. In the difference between two sexes was 98% and within each present study, polymorphic microsatellites were applied group was 2%. The genetic relationship among samples to study genetic variation, among common carp analyzed by multidimential scaling analysis of Nei, [7], population of Caspian Sea. 58

Genetic diversity is important to both natural and cultured populations because it provides the necessary spectrum of genotypes for adaptive response to changing conditions and heterozygous individuals usually are superior to less heterozygous individuals in many economically important characteristics like growth, fertility and disease resistance [11]. Therefore, there has been increasing attention being paid to loss of genetic diversity in natural resources fish stocks including carp. There are several report of analyzing the microsatellite variation in common carp [2, 3, 8, 12]. In most of these studies, there have limitations, due to the sampling of restricted number of populations or the used of small sample sizes such as the present study, therefore the levels of variation detected are broadly similar to the results of this study. Loss of variations in closed hatchery populations can occur during establishment (founder effects) and over subsequent generations though genetic drift arising from low effective broodstock number [13]. The large reduction in genetic variability in the experimental lines observed in this study, Thai et al. [14] and Kohlmann et al. [12] indicated the potential negative impact of captive breeding on domesticated common carp stocks in Vietnam and elsewhere. Thus, the low levels of genetic variations most likely reflect the difficulties in genetic management of brood stock leading to low Ne. Destruction of natural spawning ground, lead to artificial propagation of the native common carp of Caspian Sea, releasing in partial mating of population (a small part). The procedure employed allowed the application of the microsatellite technique on a few fish scales to assess polymorphism pattern through an economic, rapid and non-invasive method and without a quality loss in PCR products. It is important that the observed heterozygosity were relatively low, which are represented by the significant departure from HWE at maturity of microsatellite loci. Actually several factors will lead to deviation from HWE [15]; the first is over fishing and heavy fishing pressure of large fishes. In this regard, the common carp in the Caspian Sea suffered from excessive exploitation and resources were severely declined. It has been recognized that habitat integrity and stability are imported for fish and common carp population may highly damaged the sharp change of ecosystem of Caspian Sea but more due to human activity have been greatly changing the environment for common carp native to the main river of this lake. At present many Iranian ecologists are worried about negative impacts of sharp change of ecosystem on reproduction of common carp and some endangered species in the river, particularly with migratory characteristics. However there are several attempt to improve the recruitment of the rivers and improve the hydrological changes such as optimum current velocity, that are influence on reproduction of native common carp of Caspian Sea. The understanding of genetic diversity is one of the most important steps in managing fisheries resources and aquaculture selective breeding programs [16-18]. The data of present study might act as the base information of the genetic variations and population structure, use in future for comparing the population divergence and for conservation. It is also useful for illustration of the effect of restocking on genetic structure of common carp in Caspian Sea. ACKNOWLEDGEMENT The author thank Ch. Makhtomi, F. Laloei and M.J. Tagavi for sample collection and technical assistance. This study was support by Caspian Sea Ecology Center of Mazandran, Iran. REFERENCES 1. Tanck, M.W.T., H.C.A. Baars, K. Kohlmann, J.J. Van der Poel and J. Komen, 2000. Genetic characterization of wild Dutch common carp (Cyprinus carpio L.). Aquaculture Res., 31: 779-783. 2. Desvignes, J.F., J. Laroche, J.D. Durand and Y. Bouvet, 2001. Genetic variability in reared stocks of common carp (Cyprinus carpio L.) based on allozymes and microsatellites. Aquaculture, 194: 291-301. 3. Bartfai, R., S. Egedi, G.H. Yue, B. Kovacs, B. Urbanyi, G. Tamas, L. Horvath and L. Orban, 2003. Genetic analysis of two common carp brood stocks by RAPD and microsatellite markers. Aquaculture, 219: 157-167. 4. Thai, B.T., C.P. Burridge and C.M.. Austin, 2007. Genetic diversity of common carp (Cyprinus carpio L.) in Vietnam using four microsatellite loci. Aquaculture, 269: 174-186. 5. Moritz, C. and D. Hillis, 1990. Molecular Systematics: Context and Controversies Sinauer Associates, Sunderland, MA. 6. Nei, M., 1987. Molecular Evolutionary Genetics. Columbia University Press, New York. 7. Nei, M., 1978. Estimation of average heterozygosity and genetic distance from a small number of individuals. Genetics, 89: 583-590. 59

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