Abstract
Lionfish (Pterois volitans and Pterois miles) are the first non-native marine reef fish to become established in the Western North Atlantic and Caribbean Sea. Next-generation sequencing techniques were employed to identify 18 polymorphic microsatellite loci for P. volitans and P. miles from waters off North Carolina, USA. Allele frequencies for all 18 loci conformed to Hardy–Weinberg expectations after correction for multiple comparisons, the number of alleles ranged from 2 to 20 (mean = 7.1), and observed heterozygosities ranged from 0.200 to 0.938 (mean Ho = 0.636). All 18 loci cross-amplified DNAs from representative haplotypes of both P. volitans and P. miles, and the vast majority of alleles were shared. These are the first highly polymorphic nuclear markers described for invasive lionfish and will be useful for characterizing population connectivity and monitoring the progress of the invasion on reef habitats of the Western Atlantic.
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Indo-Pacific lionfishes (Scorpaenidae) are popular aquarium fish, and well known for their ornate beauty and venomous spines. Two species of the lionfish, Pterois volitans and Pterois miles, have invaded the Western Atlantic (Whitfield et al. 2002; Freshwater et al. 2009a; Morris 2012), and are a concern to coastal managers because of their threat to fisheries resources, native fish communities, and human health (Morris and Akins 2009; Morris and Whitfield 2009). The invasive range of lionfish has expanded annually (Schofield 2010) and it is likely that it will ultimately include the entire Caribbean, Gulf of Mexico, and subtropical western Atlantic (Ahrenholz and Morris 2010; Morris and Whitfield 2009).
Mitochondrial DNA sequence analyses of lionfish revealed that both P. volitans and P. miles haplotypes are present in the Atlantic with reduced haplotype diversity compared to their native ranges, and some population structuring related to range expansion and connectivity within the Caribbean (Hamner et al. 2007; Freshwater et al. 2009a, b; Betancur et al. 2011). Highly polymorphic nuclear markers are needed to further analyze genetic diversity and population connectivity among sites in the western Atlantic. To this end, next-generation sequencing techniques were used to identify 18 polymorphic microsatellite markers from lionfish collected off the coast of North Carolina.
Genomic DNA was extracted from ethanol preserved gill tissues using the Wizard SV Genomic DNA Purification System (Promega). Non-enriched genomic DNA was subjected to next-generation sequencing on a Roche 454 GS-FLX instrument (Roche) at the Duke University Institute for Genomic Science and Policy Genome Sequencing Facility. A total of 105,334 sequence reads were generated, 69,003 were >300 bp in length and were screened for repetitive elements using Msatcommander (Faircloth 2008). A total of 5,737 repetitive sequences were found and flanking primers designed with Primer3 software (Rozen and Skaletsky 2000). Tetrameric repeats (>6) with sufficient flanking sequence information for primer design were given priority.
Genomic DNA was amplified in 20 μl polymerase chain reactions (PCRs) as follows: 2 μl DNA, 2 μl 10× PCR Buffer (200 mM Tris, pH 8.8; 500 mM KCL; 0.1 % Triton X-100, 0.2 mg/ml BSA), 1.6 μl 25 mM MgCl2, 1.6 μl 2.5 mM dNTP’s, 0.2 μl 10 μM Forward primer, 0.8 μl 10 μM Reverse primer, 0.8 μl 10 μM labeled (FAM, NED, PET, or VIC) T3 primer (Eurofins; Applied Biosystems), and 0.2 μl Taq DNA polymerase. PCR products were indirectly labeled using Forward primers with 5′-T3 tags (ATTAACCCTCACTAAAGGGA; not shown in Table 1) and fluorescently labeled T3 primers. Reactions were run under the following conditions: 94 °C 4 min; 25 cycles of 94 °C 15 s, 62 °C 15 s, 72 °C 30 s; 8 cycles of 94 °C 15 s, 53 °C 15 s, and 72 °C 30 s; final extension at 72 °C for 5 min. All amplifications were performed using a single standard condition.
PCR products were diluted 1:3 and 2 μl mixed with 0.05 μl DNA Orange (MCLab), 0.05 μl 10 mg/ml salmon sperm DNA, and 8.95 μl water, denatured at 95 °C for 10 min, and chilled on ice. Size-fragment analysis was conducted on an ABI 3730xl DNA Analyzer (Applied Biosystems), and chromatograms scored using Genemarker v1.8 (SoftGenetics). Deviations from Hardy–Weinberg Equilibrium were calculated using Arlequin v3.2 (Excoffier and Lischer 2010). Heterozygote excess, heterozygote deficiency and linkage disequilibrium were tested with Genepop version 4.0.10 (Rousset 2008) and corrected for multiple comparisons using the sequential Bonferroni approach (Rice 1989). Presence of null alleles, stutter, and large allele dropout were assessed using MicroChecker (1,000 randomizations: Van Oosterhout et al. 2004).
Forty-eight primer pairs were screened for robust amplification using DNA from four individual lionfish samples representing both P. volitans and P. miles haplotypes. Primers showing strong polymorphic products were then used to amplify DNAs from another 74 individuals from multiple locations (North Carolina, Bahamas, and Florida). Results from 18 loci scored on a minimum of 35 individuals are presented in Table 1. The number of alleles ranged from 2 to 20 with a mean of 7.1 alleles per locus. The allele frequencies of all 18 loci conformed to Hardy–Weinberg expectations after correcting for multiple comparisons using the sequential Bonferroni method (k = 18; Rice 1989). MicroChecker indicated the presence of null alleles at three loci (Pvm4, Pvm14, and Pvm37), while no loci showed evidence of scoring errors due to stuttering or large allele dropout. Arlequin detected evidence for linkage disequilibrium in pairwise comparisons among loci in both P. volitans (22) and P. miles (28) populations.
The lionfish invasion provides an excellent, albeit unfortunate, natural experiment of population connectivity within the tropical and subtropical western Atlantic. Betancur et al. (2011) used mitochondrial haplotype analysis and the chronological progression of the invasion to test hypotheses of connectivity and breaks within the Caribbean. The resolving power of these haplotype data however are limited, especially for the invasive lionfish where strong initial and secondary founder effects are present (Hamner et al. 2007; Freshwater et al. 2009b; Betancur et al. 2011). These microsatellite markers will provide much greater resolution for exploring the invasion’s expansion and connectivity among marine organisms.
References
Ahrenholz DW, Morris JA (2010) Larval duration of the lionfish, Pterois volitans along the Bahamian Archipelago. Environ Biol Fish 88:305–309
Betancur RR, Hines A, Acero PA, Ortí G, Wilbur AE, Freshwater DW (2011) Reconstructing the lionfish invasion: insights into greater Caribbean biogeography. J Biogeogr 38:1281–1293
Excoffier L, Lischer HEL (2010) Arlequin suite ver 3.5: a new series of programs to perform population genetics analyses under Linux and Windows. Mol Ecol Resour 10:564–567
Faircloth L (2008) MSATCOMMANDER: detection of microsatellite repeat arrays and automated, locus-specific primer design. Mol Ecol Resour 8:92–94
Freshwater DW, Hamner RM, Parham S, Wilbur AE (2009a) Molecular evidence that the lionfishes Pterois miles and Pterois volitans are distinct species. J N.C Acad Sci 125:39–46
Freshwater DW, Hines A, Parham S, Wilbur A, Sabaoun M, Woodhead J, Akins L, Purdy B, Whitfield PE, Paris CB (2009b) Mitochondrial control region sequence analyses indicate dispersal from the US East Coast as the source of the invasive Indo-Pacific lionfish Pterois volitans in the Bahamas. Mar Biol 156:1213–1221
Hamner RM, Freshwater DW, Whitfield PE (2007) Mitochondrial cytochrome b analysis reveals two invasive lionfish species with strong founder effects in the western Atlantic. J Fish Biol 71:214–222
Morris JA (Ed) (2012) Invasive lionfish: A guide to control and management. Gulf and Carribean Fisheries Institute Special Publication Series Number 1, Marathon Florida USA. 113p
Morris JA, Akins JL (2009) Feeding ecology of invasive lionfish (Pterois volitans) in the Bahamian archipelago. Environ Biol Fish 86:389–398
Morris JA, Whitfield PE (2009) Biology, ecology, control and management of the invasive Indo-Pacific lionfish: an updated integrated assessment. NOAA Tech Memo NOS NCCOS 99(B):57
Rice WR (1989) Analyzing tables of statistical tests. Evolution 43:223–225
Rousset F (2008) Genepop’007: a complete re-implementation of genepop software for Windows and Linux. Mol Ecol Resour 8:103–106
Rozen S, Skaletsky H (2000) Primer3 on the WWW for general users and for biologist programmers. Method Mol Biol 132:365–386
Schofield PJ (2010) Update on geographic spread of invasive lionfishes (Pterois volitans [Linnaeus, 1758] and P. miles [Bennett, 1828]) in the Western North Atlantic Ocean, Caribbean Sea and Gulf of Mexico. Aquat Invasions 5:s117–s122
Van Oosterhout C, Hutchinson W, Willds D, Shipley P (2004) MICRO-CHECKER: software for identifying and correcting genotyping errors in microsatellite data. Mol Ecol Notes 4:535–538
Whitfield PE, Gardner T, Vives SP, Gilligan MR, Courtenay WR, Ray GC, Hare JA (2002) Biological invasion of the Indo-Pacific lionfish Pterois volitans along the Atlantic coast of North America. Mar Ecol Prog Ser 235:289–297
Acknowledgments
CKF was supported in part by the Rachel Carson Scholar Program at the Duke University Marine Laboratory. This work was supported by a North Carolina SeaGrant award to TFS (Grant #2010-1706-09), NSF award DEB-0742437 to DWF, and the NOAA National Centers for Coastal Ocean Science. The scientific results and conclusions, as well as any views or opinions expressed herein, are those of the author(s) and do not necessarily reflect the views of NOAA or the Department of Commerce.
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Schultz, T.F., Fitzpatrick, C.K., Wilson Freshwater, D. et al. Characterization of 18 polymorphic microsatellite loci from invasive lionfish (Pterois volitans and P. miles) . Conservation Genet Resour 5, 599–601 (2013). https://doi.org/10.1007/s12686-013-9860-5
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DOI: https://doi.org/10.1007/s12686-013-9860-5